• Journal of Korea Water Resources Association
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• v.36 no.4
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• pp.521-531
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• 2003

Pollutant load to Yongdam Reservoir considering rainfall effect is estimated using data collected during dry and wet days between Dec 1998 and Oct. 1999. Limit of significant rainfall was assumed to be as 10 mm/day and numbers of days of significant rainfall for each month were counted using 10 years of meteorological data of the study area. Water quality input concentrations were estimated by taking weighted averages of concentrations in dry and wet days in each month. The resulting concentrations were used as inputs for water quality modeling of Yongdam Reservoir. When rainfall effect was included average reservoir concentrations of BOD, TN and TP were increased by 70％, 5％ and 27％, respectively Considering the fact that Korea is under the significant influence of monsoon effect during the summer, it should be important to include rainfall effect in estimating pollutant input to receiving waters. This method is expected to increase reliability of annual water quality modeling results by providing realistic input data.

• Journal of Korean Society of Environmental Engineers
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• v.28 no.6
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• pp.667-676
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• 2006

The reduction of $Hg^{2+}$ in the aqueous phase results in the production of dissolved gaseous mercury(DGM), and the volatilization of DGM has been identified as an important mechanism for the loss of Hg from waterbodies to the atmosphere. Although mercury emission in the world is known to be mostly from Asia, there have been few studies of measuring DGM concentrations in lakes in Asia. In this study, DGM concentrations were measured at Juam reservoir($35^{\cir}00'N,\;127^{\circ}14'E$), Korea. The results showed that the average concentrations of DGM at the upper and down stream of the lake during summer time were $95{\pm}8\;and\;130{\pm}15$ pg/L, respectively and the concentration of total mercury(TM) at the upper and down stream was $2.1{\pm}0.7,\;1.7{\pm}0.3$ ng/L respectively. Average DGM concentration during summer time($101{\pm}14pg/L$) was approximately 5.5 times higher than that during fall($18{\pm}0.1pg/L$). The DGM concentrations ai the midstream decreased from 32 to 13.7 pg/L during rain event, while the TM concentrations increased from 2.2 ng/L to 2.7 ng/L indicating the deposition of mercury from the atmosphere. Also, the diurnal patterns between DGM concentrations and UV intensities were observed. Water temperatures and DOC concentrations were significantly related to DGM concentrations, while TM concentrations were negatively related to DGM concentrations(p<0.0001). Comparing with the study of Dill et al.,(2006) the average concentrations of DGM $(109{\pm}15pg/L)\;and\;TM(2.2{\pm} 0.4ng/L)$ at Juam reservoir were approximately 3 and 2.2 times higher than those measured in other lakes(DGM: $38{\pm}16pg/L$, TM: $1.0{\pm}1.2ng/L$).

• Proceedings of the Korea Water Resources Association Conference
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• 2008.05a
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• pp.779-784
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• 2008

환경부에서 추진하고 있는 토지피복 중분류별 비점오염부하원단위를 산정하기 위한 사업 중 나지로 분류되는 채광지역의 비점오염부하를 측정하였다. 비점오염부하는 강원도 삼척시 도계읍의 도계 작업장(석탄)과 태백시 장성동의 태백 저탄소 등 2곳의 채광지역에서 2007년 9월부터 12월까지 2회의 강우유출사상을 대상으로 측정하였다. 2회 강우사상 동안 총강수량은 도계 작업장에서 149 mm이었으며 태백 저탄소에서 201 mm이었다. 유출량은 수위계와 유량계로 5분 단위로 측정하였으며, 수질시료는 자동채수기로 2시간 간격으로 채취하였다. 수질시료는 환경부의 공정시험법에 따라 SS, BOD, CODcr, T-N, T-P, 그리고 TOC 농도를 분석하였다. 그리고 일부의 시료에 대해서는 Zn, Cb, Cu, 그리고 Pb의 농도를 분석하였다. 도계 작업장의 유량가중평균농도는 갱내수의 수질에 많은 영향을 받는 것으로 나타났다. 도계작업장의 일평균유량가중평균농도는 SS $86.3{\sim}94.9\;mg/{\ell}$, BOD $3.8{\sim}7.6\;mg/{\ell}$, COD $26.9{\sim}51.6\;mg/{\ell}$, T-N $1.5{\sim}2.1\;mg/{\ell}$, T-P $0.2\;mg/{\ell}$ 그리고 TOC $1.8{\sim}2.3\;mg/{\ell}$로 나타났다. 태백 저탄소의 일평균유량가중평균농도는 SS $16.5{\sim}66.6\;mg/{\ell}$, BOD $7.4{\sim}9.8\;mg/{\ell}$, COD $41.1{\sim}66.7\;mg/{\ell}$, T-N $0.7{\sim}1.1\;mg/{\ell}$, T-P $0.2\;mg/{\ell}$ 그리고 TOC $1.7{\sim}2.6\;mg/{\ell}$로 나타났다. 중금속의 농도는 모든 시료에서 환경부의 배출허용기준농도보다 낮게 나타나거나 검출되지 않았다. 도계 작업장의 일오염부하는 SS $1,368.8{\sim}1,984.1\;kg/day$, BOD $56.6{\sim}128.9\;kg/day$, COD $385.7{\sim}933.7\;kg/day$, T-N $23.4{\sim}44.5\;kg/day$, T-P $2.1{\sim}4.8\;kg/day$ 그리고 TOC $24.3{\sim}39.3\;kg/day$이었다. 태백 저탄소의 일오염부하는 SS $8.2{\sim}162.1\;kg/day$, BOD $2.6{\sim}15.3\;kg/day$, COD $13.8{\sim}83.6\;kg/day$, T-N $0.2{\sim}3.1\;kg/day$, T-P $0.1{\sim}0.6\;kg/day$ 그리고 TOC $0.7{\sim}4.4\;kg/day$로 나타났다. 본 연구는 2회의 강우유출사상에 대하여 측정한 자료이므로 연평균농도나 연평균오염부하로 활용하기는 어렵다. 그러나 석탄광산지역의 비점오염부하를 이해하는데 활용할 수 있으며 또한 장기적인 연구자료로 활용하여 석탄광산지역의 비점오염원단위의 산정에 유용한 자료로 활용할 수 있다.

• Korean Journal of Fisheries and Aquatic Sciences
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• v.28 no.5
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• pp.577-588
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• 1995

The chemical constituents for the seawater and sediment were measured to evaluate pollution in the sea around Pusan Harbor in winter, n992. The average value of trophic state index (TSI) was 19.4 at the outside of Buk Harbor, 50,4 at the inside of Buk Harbor, 56,3 at the Nam Harbor and 5,0 at the Kamchun Harbor. The high correlation found in salinity-nutrients diagram with AOU suggested that the enrichment of nutrients in Pusan Harbor during winter was mainly due to the influx of terrestrial effluents and partially by regenerated nutrients from suspended organic matters in the water column. The mean values of total ignition loss (TIL), COD and total sulfide in the surface sediments were$12.1\%$, 17.5 mg/g.dry wt. and 1.18 mg/g.dry wt. respectively. The highest level of those parameters was shown mostly at the inside of Buk Harbor. The mean concentration of total organic carbon (TOC), total organic nitrogen (TON), and total phosphorus were 24.9 mg/g.dry wt., 1.3mg/g.dry wt. and 0.69 mg/g. dry wt., respectively, Both of the highest level for TOC and total phosphorus have found at the Nam Harbor. On the other hand, the Highest level for TON was found at the inside of Buk Harbor. The TOC/TON atomic ratio with a range of 10.2-60.2 (mean value of 22.5) strongly indicated the active role of the input from the terrestrial organic pollutants.

• Korean Journal of Food Science and Technology
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• v.15 no.4
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• pp.342-347
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• 1983

The effects of barley tea concentration and atomizing air pressure on the size, homogeneity and distribution of the sprayed droplets were investigated. An equation relating mean diameter (${\overline{D}}$) with the concentration where the coefficient a and b were determined empirically. As the operating air pressure was increased, the mean diameter of the droplets decreased and finally reached the limiting mean diameter, $36{\mu}m$ at 15.7% barley tea concentration. The homogeneity of the droplets increased with the operating air pressure, increase and it was decreased steadily as the soluble solid concentration increased up to 20% and markedly over 20% at every operating air pressure. The distribution ($P_D$) of sprayed droplets related with the droplet size as the following exponential equation; $P_D$ = e 1nD + f where e and f are empirical constants.

• Korean Journal of Fisheries and Aquatic Sciences
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• v.7 no.3
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• pp.169-178
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• 1974

Concentrations of mercury, cadmium, lead and copper are determined in the surrounding seawater and in seaweeds, Undarta pinnatifida and Sargassun fulvellum, from Suyeong Bay in Busan in the spring tide and neap tide from January to April 1974. The range and mean of the heavy metal concentrations in the surrounding seawater are as follows : mercury 0.00-0.39 ppb, 0. 16ppb; cadmium 0.00-0.46 ppb, 0.18 ppb, lead 0.00-0.94 ppb, 0.26 ppb : copper 0.00-0.86 ppb, 0.25 ppb respectively, and the concentrations varied slightly according to the tide. The mean values of concentration rate of Hg, Cd, Pb and Cu in air dry base were $0.42\times10^3(0.13\times10^3\~1.0\times10^3)$, $2.1\times10^3(0.8\times10^3\~4.9\times10^3)$, $8.9\times10^3(3.1\times10^3\~19\times10^3)$ and $15\times10^3(6.0\times10^3\~28\times10^3)$ in the Undaria pinnatifida, and $0.25\times10^3($0.06\times10^3\~0.56\times10^3)$, $1.0\times10^3(0.61\times10^3\~1.7\times10^3)$, $5.4\times10^3(3.1\times10^3\~8.5\times10^3)$ and $22.8\times10^3(14.4\times10^3\~52.4\times10^3)$ in the Sargassun fulvellum. The concentration rate of Hg, Cd and Pb of the Undaria pinnatifida was almost twice as much as that of the Sargassun fulvellum but the concentration rate of copper of the former was slightly smaller than of the latter.

• Proceedings of the Korea Air Pollution Research Association Conference
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• 2003.11a
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• pp.299-300
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• 2003

지난해 수도권에서 월드컵경기가 진행되었던 2002년 6월 6일에 구리 수택동 지점에서 203ppb에 이르는 고농도 오존이 발생하였다. 이때의 기상상태는 바람이 약하고 일사량이 강하고 운량이 적는 둥 고농도 오존의 좋은 조건이었다. 반면 2002년 7월 27일은 6월의 경우와 마찬가지로 기상조건은 고농도 오존생성의 호조건이었으나 수도권 67개 지점의 오존 평균 농도가 30ppb이하의 낮은 농도를 나타내었다. 본 연구에서는 광화학모델인 Models-3/CMAQ을 이용하여 이러한 2가지 오존 사례를 모사하고 특징을 비교 고찰하고자 한다. (중략)

• Journal of Korean Society of Environmental Engineers
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• v.28 no.11
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• pp.1135-1140
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• 2006

Concentration and speciation of trihalomethanes(THMs) and haloacetic acids(HAAs) that can be created during chlorine disinfection as disinfection by-products(DBPs) in Korean water treatment plants(WTPs) were investigated. 4 WTPs that adopted conventional water treatment processes were chosen for investigation and each represented a typical WTP on the Han, Keum, Sumjin and Nakdong Rivers. The average concentration of THMs was 26.9 ppb, and the maximum and minimum concentrations were 47.6 ppb and 11.0 ppb respectively, while the average concentration of HAAs was 25.4 ppb, and the maximum and minimum concentrations were 57.1 ppb and 9.7 ppb respectively. DBPs concentration was lower in the winter than the summer. The major species of THMs was chloroform and its average percentage was 77%, and the second highest was bromodichloromethane(20%), while the concentration of bromoform was below detection limits. The sum of dichloroacetic acid(DCAA) and trichloroacetic acid(TCAA) was 97% of $HAA_5 $ on average base. But its percentage was 90% in the Han River WTP, especially it was the lowest during the winter. On the other hand, the concentration of DCAA was higher than TCAA except during the summer.

• Korean Journal of Environment and Ecology
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• v.24 no.5
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• pp.539-546
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• 2010

To investigate the variation of anion concentrations in relation to forest type, forest-related factors, forest survey and anion concentrations measurement were carried out on the 52 quadrats located at the national forest areas in Yangyang-gun, Kangwon-do. The relationship between anion concentrations and forest-related factors were correlated. Total mean of anion concentration was 2,405 ea/$cm^3$, which was slightly higher than general figures 2,000ea/$cm^3$. Highly significant positive correlations were observed between anion concentrations and soil moisture contents, and also between anion concentrations and altitude. Significant positive correlations were observed between anion concentrations and topography. Anion concentrations were significantly different among soil moisture levels. Mean anion concentration were highest at 4,524.4ea/$cm^3$ in on wet sites, and followed slightly wet sites and moderate sites. Mean anion concentrations was highest on valley sites at 3,372.4ea/$cm^3$, followed by slope and ridge areas. Mean anion concentrations measured before noon was highest at 3,133.4ea/$cm^3$, and measurements during 12:00~15:00 and after 15:00, showed relatively low anion concentrations. Mean anion concentrations was highest at mixed deciduous forests at 3,503.9ea/$cm^3$, followed by oak forests, pine forests, and pine-oak forests. Results of this study are expected to be used in planning therapeutic forests.

• Journal of Preventive Medicine and Public Health
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• v.29 no.3 s.54
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• pp.693-700
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• 1996

The purpose of this study was to determine whether workers at a factory next to a lead recycling factory in Pusan, were affected by lead contamination. The mean air lead concentration of lead recycling factory was $0.21mg/m^3(TWA=0.05mg/m^3)$. Thirty-nine male workers of Factory A, Cr. plating factory next to the lead recycling factory were exposed group and a comparison group, 62 male workers of Factory B were selected from another Cr. plating factory about 8.5km away from lead recycling factory. Air lead concentration of each workplace was checked for 4 times from August f to August 20 in 1995 by low volume air sampler. Each subject was interviewed about age, life-style, smoking, work history, and residence etc, and venous blood was drawn for lead measurement by graphite furnace atomic absorption spectrometry. We have observed that air lead concentration and blood lead concentration of Factory A was higher than Factory $B(2.6{\pm}1.6\;Vs.\;1.2{\pm}0.2{\mu}g/m^3,\;14.9{\pm}1.6\;Vs.\;12.2{\pm}1.6{\mu}g/dl)$. We believe that other environmental lead sources such as transportation and residence did not affect air lead and blood lead concentration differences of both factory. We concluded that high air lead and blood lead concentration of Factory A were caused by lead contamination generated by the neighboring lead recycling factory.