• 한국물환경학회지
• /
• 제27권1호
• /
• pp.36-43
• /
• 2011

This study is selected two points of combined sewer that occurred Fish Kill after first flush, that analyzed generation of pollutants and stream runoff generation of combined sewer overflows (CSOs) as fine weather and rainfall. In addition, this study was to analyze the relationship between CSOs and sediments, to propose measures to reduce the sediment relevant with CSOs and rainfall runoff from entering sewage treatment plants and measures for discharged directly into streams when indicate relatively good water quality after overflow. Sediments in combined sewer system was discharged about 50~80% as overflows during rainfall and we can reduce the amount of the CSOs at least 50% or more if the sewer does not exist in the sediments because of the amount of discharge about the amount of intercept has been investigated by 3~5 times. Because of velocity at sediment interval in sewer is very low, sewage velocity of about 3~5 times as much as it can increase the amount of sediment can be reduced if the separation wall is installed. Effective control of BOD overflow load is respectively 77.5%, 75.8% at first point, second point by the separation wall is installed. Drainage area greater than area in this study or many combined sewer overflows region is increased the more effective control of separation wall. Turbidity to measure changes in water quality of overflows can be used as an factor to control the intercept flows because the intercept flows(3Q) after the first flush has lowered removal efficiency and increases the operational load of sewage treatment plants. Sewage water quality after a overflow when the reasonable turbidity was measured at this point flows to excluded intercept flow(1Q) can be discharged to stream.

• 한국수자원학회논문집
• /
• 제40권5호
• /
• pp.397-407
• /
• 2007

건기 때의 합류식 관거 내 고형물의 퇴적으로 인해 통수능이 감소하여 여름철 우기시 국지적인 침수가 발생하며 이로 인해 관거 내 퇴적을 더욱 초래할 수가 있다. 이와 같은 문제를 해결하고 관거 시스템을 효율적으로 관리하기 위해서는 관거 내 고형물 퇴적량을 산정하기 위한 식을 개발할 필요가 있다. 그러나 이러한 산정식을 개발하기 전에 컴퓨터 모형 등을 이용한 고형물 퇴적량을 산정하여야 한다. 따라서 본 연구에서는 국내 군자매수유역에 대해 MOUSE 모형을 적용하여 관거 내 고형물 퇴적량을 산정하였으며, 이를 미환경보호청(EPA)에서 개발한 산정식을 이용하여 산정한 퇴적량과 검토하였다. MOUSE 모형을 적용하여 산정한 값은 EPA에서 1977년에 개발한 초기의 산정식에 의한 결과보다는 작지만 1984년에 개발된 산정식에 의한 결과보다는 다소 크게 나타나고 있다. 퇴적고형물의 관측자료가 구비되어 있지 않아 모형에 의한 산정치를 비교하기는 곤란하지만 모형에 의해 산정결과가 신뢰성이 있다고 판단되며, 추후 군자배수유역에 대한 산정식을 유도하는데 이용할 수 있다고 본다.

• Environmental Engineering Research
• /
• 제18권2호
• /
• pp.71-75
• /
• 2013

This study is to evaluate the effects of the separation wall on the sediment quality and quantity in a combined sewer, by surveying the sewer overflow and sediments during a rainfall. Since the separation wall installed in the combined sewer separates the rainfall and the sewage, the flow rate of the sewage is increased, and the amount of the sediment deposited on the sewer is decreased. One sampling point was the outfall of Daesacheon with a separation wall, and the other was the outfall of Gwaryecheon without a separation wall, in Daejeon metropolitan city. The maximum control of the biochemical oxygen demand (BOD) overflow load was more than 38% in the Daesacheon point with the separation wall, during a rainfall of 0.11 mm/hr. The maximum control of the BOD overflow load was 24% in Gwaryecheon without a separation wall, during a rainfall of 1.0 mm/hr. According to the survey results of the sediment in the sewer, the discharged sediment deposited on the sewer in Gwaryecheon point was about 23% to 28% of the total suspended solid during the rainfall. In addition, the average velocity of sewage in the presence of sediment was about 0.30 m/s, and if the separation wall is installed, it was expected to be about 1.01 m/s, that is 3.4 times more than the same conditions, resulting in the reduction of the sediment deposit.

• 상하수도학회지
• /
• 제10권3호
• /
• pp.83-91
• /
• 1996

The pulverized wastes originated from kitchen garbage grinder cause an additional load in sewage treatment plant and water environment. Therefore, several problems occur in sewer, such as microbial corrosion, odor, psychoda and fly interrupting flow of sewage etc. by their precipitation with earth and sand. This study was conducted on two experiments: hydrogen sulfide gas generation from sediments in sewer and anaerobic batch test. In anaerobic batch test, gas generation was increased when organic compounds were increased in concentration. Sulfide was decreased upon decreasing in sulfate concentration. In $H_2S$ gas generation test along the depth of sediments there were two different sampling sites which are apart from about 50 cm each other in a menhole. The one has the thickness of 55 cm from the surface, the other, of 60 cm. The hydrogen sulfide gas production rates were measured based on ranges from 0 to 10 cm, 10 to 20 cm, 20 to 30 cm for two samples. The results obtained were 1.08, between 0 to 10 cm in depth for the sample thickness of 55 cm and 3.07, 5.36, $5.42{\mu}g/g-VS{\cdot}hr$ in order of depth for the sample thickness of 60 cm, respectively.

• 한국대기환경학회지
• /
• 제27권6호
• /
• pp.703-710
• /
• 2011

Odor emission from domestic sewer systems has become a serious environmental problem. An investigation on a sewer manhole revealed that anaerobic decay of sediment organic matters (SOMs) and related declines of oxidation reduction potential (ORP) in the sediment layer were the main reason of the production of volatile sulfur compounds. In addition, as the anaerobic decaying period continued, the odor intensity rapidly increased with increasing concentrations of $H_2S$ and dimethyl sulfide. As a feasible method to control SOMs and to minimize odor emission potentials, an electrolytic oxidation process has been employed to the sediment sludge phase. In this study, voltages applied to the electrolytic oxidation process were varied as a main system parameter, and its effects on odor removal efficiencies and reaction characteristics were investigated. At the applied voltages greater than 20 V, the system efficiently oxidized the organic matter, and the ORP in the sludge phase increased rapidly. As a consequence, the removal efficiency of hydrogen sulfide was found to be >99% within 60 minutes of the electrolytic oxidation. Overall, the electrolytic oxidation process can be an alternative to control odor emission from sewer systems, and a threshold input energy needs to be determined to achieve effective operation of the process.

• 융합정보논문지
• /
• 제10권7호
• /
• pp.153-159
• /
• 2020

본 연구에서는 실제 하수관로 내 흐름상태를 파악하기 위하여, 건기동안 처리구역 최상부에 위치한 관로의 수위, 유속, 유량의 값을 실제 측정하여 추정된 하수의 전단응력을 조사하였다. 수세분뇨 및 토사를 모사하기 위해 점착성 및 비점착성 고형물(두부와 모래)을 따로 또 함께 투입한 후 흐름의 상태를 촬영하였는데, 본 실험대상관로에서는 큰 방해없이 침전물이 하수와 함께 씻겨 내려가는 것을 관찰하였다. 경사가 0.00319인 관로에서 주중 하수의 최소전단응력을 초과하는 빈도는 0이었고 0.00603의 기울기의 경우 10회였다. 현장조사기간 중 최소전단력을 초과하는 이벤트는 1회 발생하여 하수도에서 악취가 증가될 가능성을 시사하였다. 경사가 가파른 관로의 최대전단응력은 2.9~3.1N/㎡이었지만, 완만한 경사에서는 1.6~1.7 N/㎡으로 감소하였다. 강우시 합류식 관로로 유입될 수 있는 비응집성 입자를 포함한 하수는 최소전단응력 기준 이하로 유지되는 시간 간격이 주중에 비해 주말동안 증가하였다. 설계기준에 따라 설계된 본 실험대상 관로에서는 수세분뇨가 직투입되어도 관로내 침전물이 오래 퇴적상태로 머물지 않고 하수와 함께 흘러갈 수 있음을 확인할 수 있었다.

• 상하수도학회지
• /
• 제33권2호
• /
• pp.121-129
• /
• 2019

If sewage flows for an extended time at low velocities, solids may be deposited in the sewer. Sufficient velocity or tractive force should be developed regularly to flush out any solids that may have been deposited during low flow periods. This study aims to evaluate the periods (T) during which sewage flow greater than the minimum tractive force maintains on a spot in sewer pipe system with lower tractive force or lower velocity than expected in the design step, when a storage tank installed in a place upsteam pours water into the sewer. The effect to T of design factors of storage tank and sewer pipes was evaluated assuming the uniform flow in sewers. When the area of orifice in the storage tank is $0.062m^2$(or 0.28 m diameter), the maximum T of 31sec was maintained using the usually used preset range of values of several design factors. As the horizontal cross section of storage tank and water depth of storage tank and roughness in sewers increase, T linearly increases. Also, T linearly decreases as the diameter of a sewer pipe increases. Although T gradually decreases as the sewer pipe slope decreases to around 0.005, T decreases sharply when the slope is less than 0.003.

• 한국수자원학회논문집
• /
• 제39권6호
• /
• pp.533-544
• /
• 2006

합류식 관거 내 고형물의 퇴적으로 인해 통수능이 감소하여 여름철 장마시 국지적인 침수가 발생하며 이로 인해 관거 내 퇴적을 더욱 초래할 수가 있다. 이와 같은 문제를 해결하고 관거의 적절한 유지관리를 위해서는 배수유역에서의 하수 및 지표면으로부터의 고형물 부하량을 산정할 필요가 있으나 많은 비용과 노력이 수반되어야 한다. 따라서 본 연구에서는 미국환경보호청에서 제시한 건조기의 합류관거 내 고형물 퇴적 부하량 산정기법과 지표면에서의 고형물 부하량 산정기법을 우리나라 군자배수유역에 적용하여 분석하였다. 분석결과 하수로부터의 고형물 부하량은 205,759ka/yr이고 지표면으로부터의 고형물 부하량은 1,321,993kg/yr로 총 1,527,752kg/yr로 나타났다. 또한 수거량은 1,486,636kg/yr로 나타나 적절한 산정결과를 보여주었다. 배수유역에서 관거 및 지표면에서의 장기적인 관측이 이루어지고 이에 따라 국내설정에 맞도록 산정공식의 수정이 이루어지면 더욱 신뢰성 있는 산정을 할 수가 있으며 이를 통해 실무에서 많은 비용과 노력을 줄이고 합류식 관거 유지관리를 할 수가 있겠다.

• 한국수자원학회논문집
• /
• 제39권5호
• /
• pp.405-415
• /
• 2006

건조기 때의 합류식 관거 내 고형물의 퇴적으로 인해 통수능이 감소하여 여름철 장마시 국지적인 침수가 발생하며 이로 인해 관거 내 퇴적을 더욱 초래할 수가 있다. 또한 관거 시스템에 퇴적된 고형물로 인해 우기시 'first-flush' 현상을 초래하기도 한다. 이와 같은 문제를 해결하기 위해서는 장기간에 걸친 관거 내 고형물 퇴적량을 관측할 필요가 있으나 많은 비용과 노력이 수반되어야 한다. 따라서 본 연구에서는 미국환경보호청에서 개발한 건조기의 합류관거 내 고형물 퇴적량 산정기법을 우리나라의 배수유역에 적용하여 분석하였다. 분석결과 적용 배수유역의 가용 자료에 따라 모형을 선택하여 실무에서 간편하게 적용할 수가 있지만 모형별 변수산정 방법별로 많은 차이를 보이고 있다. 초기에 유도된 Eqs. (1)$\sim$(4)가 후에 유도된 Eqs. (5)$\sim$(9)보다 산정치가 모두 크게 나타나고 있으며 전반적으로 중간모형이 정밀모형이나 단순모형보다 크게 나타나고 있다. 건조기 동안의 관거 내 퇴적고형물의 관측자료가 구비되어 있지 않아 실질적으로 비교하기가 곤란하지만 대상 배수유역 관거에서의 장기적인 관측이 이루어지고 이에 따라 국내실정에 맞도록 산정공식의 수정이 이루어지면 실무에서 많은 비용과 노력을 줄이고 관거 관리를 할 수 있다고 판단된다.

• 상하수도학회지
• /
• 제28권6호
• /
• pp.647-655
• /
• 2014

To perform long-term sewer monitoring, It is important to understand the nature of the wastewater flow that occurs at the point on early stage of the monitor and to prevent in advance a problem which may caused. We can infer the flow properties and external factors by analyzing the scatter graph obtained from the measured data flow rate monitoring data since an field external factor affecting the sewage flow is reflected in the flow rate monitoring data. In this study, Selecting the three points having various external factors, and we Inferred the sewer flow characteristics from depth-velocity scatter graph and determined the analysis equation for the dry-weather flow rate data. At the'point 1' expected non-pressure flow, we were able to see the drawdown effect caused by the free fall in the manhole section. At the'point 2', existed weir and sediments, there was backwater effect caused by them, and each of size calculated from the scatter graph analysis were 400 mm and 130 mm. At the'Point 3', there is specific flow pattern that is coming from flood wave propagation generated by the pump station at upstream. In common, adequate equations to explain the dry weather flow data are flume equation and modified manning equation(SS method), and the equations had compatibility for explaining the data because all of $R^2$ values are over 0.95.