• 한국환경과학회지
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• 제25권1호
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• pp.31-40
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• 2016

The purpose of this study was to analyse the runoff characteristics of non-point pollution sources in an urban watershed and determine the effectiveness of newly installed riverwater treatment system to reduce water pollution caused by storm runoff in the urban watershed. The results of this study showed that the levels of BOD5 and suspended solid were highly influenced by first-flush effect and the pollutant load of those two parameters were also very high in the urban watershed. Meanwhile, the effectiveness of riverwater treatment system to reduce the levels of BOD5 and suspended solid was relatively high, but those to reduce the levels of T-N and T-P was low, which needs some additional unit treatment process such as filtration and coagulation. Nonetheless, the riverwater treatment system tested was relatively simple in installation and operation, effective in removing many water pollutants and, most importantly, does not require much space as other treatment systems, so it could be an attractive alternative option to reduce riverwater pollution caused by storm runoff in urban watersheds.

• Steel and Composite Structures
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• 제28권2호
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• pp.209-221
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• 2018

An empirical and efficient method is presented for calculating the dynamic increase factor to amplify the applied loads on the affected bays of a steel frame structure with semi-rigid connections. The nonlinear static alternate path analysis is used to evaluate the dynamic responses. First, the polynomial models of the extended end plate and the top and seat connection are modified, and the proposed polynomial model of the flush end plate connection shows good agreement as compared with experimental results. Next, a beam model with nonlinear spring elements and plastic hinges is utilized to incorporate the combined effect of connection flexibility and material nonlinearity. A new step-by-step analysis procedure is established to obtain quickly the dynamic increase factor based on a combination of the pushdown analysis and nonlinear dynamic analysis. Finally, the modified dynamic increase factor equation, defined as a function of the maximum ratio value of energy demand to energy capacity of an affected beam, is derived by curve fitting data points generated by the different analysis cases with different column removal scenarios and five types of semi-rigid connections.

• 산업기술연구
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• 제27권B호
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• pp.83-89
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• 2007

We studied runoff characteristics of combined sewer overflows in a city while it was raining. The event mean concentration (EMC) of biochemical oxygen demand (BOD), chemical oxygen demand ($COD_{Cr}$), suspended solids (SS), total nitrogen (TN), and total phosphorus (TP) in one of the combined sewer sites in Chuncheon was 63.5-211.6 mg/L, 114.9-523.8 mg/L, 70.3-436.4 mg/L, 6.4-33.0 mg/L, and 1.09-6.81 mg/L, respectively. In another combined sewer, the EMC of BOD, COD, SS, TN, and TP was 42.1-131.4 mg/L, 107.7-256.5 mg/L, 33.7-221.1 mg/L, 7.9-26.4 mg/L, and 1.16-3.91 mg/L, respectively. The ratio of the cumulative pollutant mass and the cumulative discharged volume determined using all parameters (BOD, $COD_{Cr}$, SS, TN, and TP) was over 1.0, which shows the first flush effect. Relationships between flow and loadings of BOD, $COD_{Cr}$, SS, TN, and TP were 0.90, 0.89, 0.88, 0.89, 0.92, respectively. Although the size of two areas was almost same, pollutant concentration and loading were different because of the amount of rainfall, rainfall intensity and basin area.

• 한국물환경학회지
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• 제33권4호
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• pp.474-480
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• 2017

This study was to estimate the reduction effect of nonpoint source pollutants according to the rainfall intensity and drainage of infiltration grate inlet. Soil infiltration flow was measured on-site and SS load by the filter part was calculated by the experimental data in laboratory reactor test. Soil infiltration flow was measured to be about $1m^3/hr$ in soil condition saturated with water. The filter part of the infiltration grate inlet was a hydraulic equipment unhindered by soil infiltration on the bottom of the storage tank, because the infiltration flow was measured to be about $3m^3/hr$ continuously in the closing infiltration hole condition. Infiltration flow and SS load were over about $1m^3/hr$ and 1.71 kg according to laboratory results by the filter part using the artifical sample. Therefore, the above values could be presented as the limitted value to start the reduction of filtration effect. Reduction efficiencies of SS load by the filter part for the rainfall intensity were about 87 % at 5 mm/hr and about 61 % at 10 mm/hr in consideration of one infiltration grate inlet got the drainage area about $200m^2$. The reduction efficiency of nonpoint source pollutants was very effective in the first flush rainfall. However, the reduction efficiency by rainfall density was higher than by flow.

• 한국환경과학회지
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• 제13권3호
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• pp.251-262
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• 2004

To identify the characteristics of wastewater flow generated in treatment basins of Seogwipo-city, we selected 3 stations representing the basin and performed 7 times of field survey including 5 times in dry periods and 2 times in wet periods from Feb. 25 to May 27, 2002 for the selected stations. From the analysis of flow data measured for more than 60 days in the interval of 5 minutes and concentration data obtained from laboratory analysis, we can draw several conclusions. First, in the analysis of diurnal variation of wastewater flow for land-use types, we could find the following results: in the residential area, it is observed that wastewater flow rates rise early in the morning for the office-going hour and fall gradually and rise again after the office-leaving hour, showing typical residential wastewater flow pattern, while for the residential and commercial area flow rates rise early in the morning at the office-going hour and move up and down repeatedly within wide range and last till the office-leaving hour, which can be resulted from wastewater that is generated by tourists activated after early in the afternoon, while for the touristy area flow rates rise early in the morning and fall gradually and rise again within wide range. Second, in the analysis of temporal variation of wastewater flow for monthly, it can be observed that in the residential area, in the residential and commercial areas the flow rate of May is higher than that of Feb., March, while for the touristy area flow rate is without monthly because it reflects the movement of population, Third, in wet periods concentration of water-quality item such as SS, BOD, and COD_{cr}$ is high in the beginning of rainfall by first flush, and falls down gradually to reach the steady state, which is the level of wastewater in dry periods after the cease of storm water due to diluting effect resulting from additional runoff water through storm sewers.

• 한국수자원학회:학술대회논문집
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• 한국수자원학회 2021년도 학술발표회
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• pp.284-284
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• 2021

비점오염원이란 도시, 도로 포장면, 무허가 가축시설, 무단 경작지 등의 불특정 장소에서 불특정하게 발생하는 오염원을 말한다. 이러한 비점오염원은 주로 강우특성(강수량, 강우강도, 강우지속시간 등)에 영향을 받는 특징을 가지고 있다. 강우시 비점오염원은 주로 불투수면적에서 오염물질이 주변 하천이나 호수에 유입되어 수생태계에 악영향을 미치게 된다. 비점오염원 중 도로 노면에서 발생하는 오염물질은 농지나 가축시설에서 발생하는 오염물질(부유물질 및 유기물) 등과 달리 주로 차량에서 발생하는 오염물질이 주를 이루고 있다. 강우시 토양의 수분포화가 충분히 이루어진 후 강우강도에 따라 유출이 발생하는 농경지와는 달리 도로 노면 유출수는 누적된 오염물질들이 강우시 한꺼번에 유출되기에 강우 초기 채수 간격을 짧게 하여 수질을 분석하는 것이 중요하다. 이에 본 연구에서는 강원도 횡성군을 관통하는 영동고속국도의 횡성휴게소 불투수 노면에서 발생하는 비점오염물질을 알아보기 위해 모니터링 후 수질분석으로 노면 유출수 성분을 알아보고, 오염부하량을 계산하여 유량가중평균농도(EMC, Event Mean Concentration)와 초기세척효과(Mass First Flush effect)을 산정하였다. 이후 타 토지이용에서의 유출 특성과 고속국도 휴게시설에서 발생하는 비점오염물질의 유출 특성에 대해 분석하였다. 추후 본 연구자료는 고속국도와 주변 편의시설 설계시 주변 수생태계에 미치는 영향에 대한 기초자료로 활용할 수 있을 것이다.

• 대한토목학회논문집
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• 제4권2호
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• pp.45-53
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• 1984

본(本) 연구(硏究)는 우리 나라에 있어서의 도시(都市)와 농촌(農村)의 비점원(非點源) 오염물질(汚染物質) 배출량(排出量)과 강우시(降雨時) 유출(流出)에 따르는 농도(濃度)의 양상(樣相)을 조사(調査)하였다. 주요분석항목은 COD, BOD, SS 이었으며 1981년(年) 5월(月)부터 8일(日)까지 수행(遂行)되었다. 도시지역(都市地域)의 비점원(非點源) 오염물질(汚染物質) 배출량(排出量)은 강우강도(降雨强度)와 강우지속시간(降雨持續時間) 등이 영향을 주었는 데 초기우수(初期雨水)에서 그 농도(濃度)는 유량(流量)이 증가(增加)함에 따라 높아지는 양상(樣相)을 띤다. 또, 집중강우시(集中降雨時) 유량(流量)이 급격히 증가(增加)하더라도 그 농도(濃度)는 희석되기 때문에 그만큼 증가(增加)하지 않는다. 최대강우(最大降雨) 이후(以後) 다시 새로운 강우(降雨)가 형성(形成)될 때 오염물질(汚染物質)의 농도(濃度)는 초기강우(初期降雨) 이전(以前)의 농도(濃度)보다 낮은 경우가 있는데 이것은 하수천(河水川) 및 하수거(下水渠)에 침적된 오염물질(汚染物質)이 강우(降雨)에 의해 씻어 내려갔기 때문이다. 그러나 최대유량(最大流量) 이후(以後) 초기강우(初期降雨)보다 큰 강우강도(降雨强度)가 지속(持續)되는 경우에는 유량(流量)이 증가(增加)함에 따라 오염물질(汚染物質)의 농도(濃度)가 증가(增加)한다. 도시지역(都市地域)의 강우시(降雨時) 면적당(面積當) 비점원(非點源) 오염물질(汚染物質)의 배출량(排出量)은 COD 489.9~1.328 kg/ha/yr로 평균(平均) 690.5 kg/ha/yr이고, BOD 226.8~614.8 kg/ha/yr로 평균(平均) 319.7 kg/ha/yr이고, SS 589.7~1,598.5 kg/ha/yr로 평균(平均) 831.2 kg/ha/yr로 산출된다. 농촌지역(農村地域)에서는 침전(沈澱)되었던 생활하수(生活下水), 퇴비 침출수 및 기타 농업폐기물(農業廢棄物) 등에 의해서 오염물질(汚染物質)이 흘러나온다. 논의 경우 면적당(面積當) 비점원(非點源) 오염물질(汚染物質) 배출량(排出量)은 COD 21.7~114 kg/ha/yr로 평균(平均) 62.34 kg/ha/yr이고, BOD 9.53~34.5 kg/ha/yr로 평균(平均) 18.65 kg/ha/yr이며, SS 8.35~29.57 kg/ha/yr로 평균(平均) 16.12 kg/ha/yr로 나타났다. 한편, 경작지의 경우 COD 46.3~171.8 kg/ha/yr범위로 평균(平均) 91.9 kg/ha/yr이고, BOD 11.7~42.5 kg/ha/yr범위로 평균(平均) 22.98 kg/ha/yr이고, SS 11.4~43.4 kg/ha/yr범위로 평균(平均) 23.09로 나타났다. 축산지역(畜產地域)의 오염물질(汚染物質)은 강우시(降雨時) 가축(家畜) 및 청소수(淸掃水), 퇴비국물에 기인한다. 면적당(面積當) 비점원(非點源) 오염물질(汚染物質) 배출량(排出量)은 COD 2,489~6,658 kg/ha/yr로 평균(平均) 3,804 kg/ha/yr이고, BOD 464~2,900 kg/ha/yr로 평균(平均) 2,047 kg/ha/yr이며, SS 729~1,442 kg/ha/yr로 평균(平均) 1,149 kg/ha/yr로 나타났다. 산림지역(山林地域)의 오염물질(汚染物質)은 강우시(降雨時) 나뭇잎이 퇴적되어 형성(形成)된 유기물층(有機物層)으로부터, 침출수(浸出水)가 씻겨져 내려오는 경우이다. 면적당(面積當) 비점원(非點源) 오염물질(汚染物質)의 배출량(排出量)은 COD 5.45~18.56 kg/ha/yr로 평균(平均) 9.86 kg/ha/yr이고, BOD 1.67~7.54 kg/ha/yr로 평균(平均) 3.48 kg/ha/yr이며, SS 9.74~10.35 kg/ha/yr로 평균(平均) 4.64 kg/ha/yr로 나타났다.

• 대한환경공학회지
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• 제36권3호
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• pp.178-184
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• 2014

본 연구에서는 기존 CSOs (Combined Sewer Overflows) 모니터링에 비해 비용효과적이며 유지관리가 용이한 모니터링 시스템 구축의 적용성 검토를 위해 10.2 ha 규모의 배수면적이 포함된 우수토실에서 2회의 강우이벤트에 대해 전기전도도 데이터 및 토연모델을 이용하여 CSOs 유량 및 수질을 예측하였다. 강우이벤트별 전기전도도 희석률에 의한 유량예측결과 실측값과의 결정계수($R^2$)는 모두 0.86 이상으로 나타났으며, 다양한 강우이벤트에 적용이 가능한 예측식 산정을 위해 선행건기일수 및 강우지속기간 2가지를 추가 매개변수로 고려하여 회귀식을 보정한 후 적용한 결과 전기전도도 희석률만을 고려한 결과에 비해 $R^2$는 0.50에서 0.80, 오차범위 40% 이내에 포함된 상대오차 누적빈도는 54.1%에서 68.5%로 예측값의 정확도가 개선되었다. CSOs 수질은 별도의 입력자료 없이 매개변수의 보정만으로 예측값 산정이 가능한 토연모델을 적용한 결과 강우 이벤트별 실측값과의 $R^2$는 BOD 0.64~0.97, SS 0.70~0.95의 범위를 나타내었다.

• 대한치과보철학회지
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• 제36권1호
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• pp.64-80
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• 1998

The risk of cross-contamination in dental clinic is very high. Those who are engaged in dental clinic are exposed to various microorganisms in saliva and blood of patient. Potential possibility of cross-contamination of patient to patient, patient to dentist, dentist to laboratory technician always exist, which is important in the view of public health. It is well known that microorganisms may cause cross-contamination by suck-back of microorganisms into the water supply line or air supply line of dental unit and sprayed back into the next patient's oral cavity. The majority of microorganisms coming from dental unit are water microorganisms from the main water supply which have colonized the tube within the units and multiplied in the relatively warm and stagnant conditions. The purpose of this study is to measure the extent of microbial contamination of dental unit and ultrasonic scaler, to evaluate that dental unit water supply is suitable for drinking water, and to assess the effect of flushing on reduction of microbial contamination of dental unit and ultrasonic scaler. In the first experiment, water samples(50ml) from 20 dental units and 10 ultrasonic scalers in Seoul National Univ. Hosp. were tested for the presence of coliform. The samples were filtered by membrane filtration technique.(Microfil system, Millipore Co. U. S. A.) The filter was then placed onto MacConkey agar plate and the plates with filter on it were incubated aerobically at $37^{\circ}C$ for 5 days. The colors and shapes of colonies were examined if those were coliform. To verify the presence of coliform, the colonies were inoculated into phenol red lactose broth and incubated aerobically at $37^{\circ}C$ for 2 days. The fomation of gas was observed. In the second experiment, water samples from 20 handpieces, 10 ultrasonic scalers and 30 A/W syringes after 0, 2, 4, 6 min. flushing respectively were taken. $200{\mu}l$ water samples were spreaded on Brain Heart Infusion agar plate and the plates were incubated aerobically at $37^{\circ}C$ for 5 days. The number of colony was counted. The results obtained were summarized as follows 1. The water from dental unit and ultrasonic scaler was not suitable for drinking water. 2. No coliform was founded in dental unit and ultrasonic scaler water supply. 3. The number of colony of dental unit and ultrasonic scaler was highest in the group of o min. flushing(p<0.05). 4. There was no statistically significant difference in the extent of microbial contamination among handpiece, ultrasonic scaler and A/W syringe (p>0.05). 5. The number of colony was lowest in the group of 4 min. flushing, but there was no statistically significant difference among 2, 4, 6 min. flushing groups.(p>0.05) 6. It is recommended to flush dental unit water line for 4 min. after use on each patient.

• 대한환경공학회지
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• 제27권12호
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• pp.1340-1346
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• 2005

소수계 물관리 진단시스템, CREEK-1을 이용하여 합류식 하수관거 월류수 발생시 청계천에서 나타나는 수질변화에 관한 모델 연구를 수행하였다. CREEK-1은 지리정보시스템, 데이터베이스, 경관생태모델(FRAGSTATS), 유역모델(SWMM), 수질모델(WASP5), 그리고 컴퓨터 그래픽으로 구성되어있다. 본 연구에서는 강우시 청계천의 수질변화를 시뮬레이션하기 위해 유역모델과 수질모델이 주로 사용되었다. 유역모델에서 청계천 전체 유역이 18개의 소유역으로, 수질모델에서 대상 하천 구간은 11개의 구획으로 나누어져 모델이 구성되었다. 유역모델은 강우시 현장에서 관측된 BOD, 총질소, 총인 그리고 유량 자료로 타당성이 검토되었으며, 그 결과 모든 항목에서 모델 예측같은 관측값과 비교적 적절한 일치를 보였다. 연구 결과는 하천의 수질이 강우량과 강우 시작 후 경과 시간에 따라 변화가 일어나고 있음을 보여주었다. 강우 초기에는 유역의 초기 세척수와 CSO에서 차지하는 하수 비율이 높기 때문에 수질이 크게 악화되었으나 유출 수량이 증가함에 따라 희석효과에 의해 수질이 개선되는 것으로 나타났다.