The purpose of this study is to investigate the ELF-MF emissions from UCLs and to compare the ELF-MF emission levels of HVTLs and UCLs. In addition, this study proposes a method and management plan to investigate the effects of exposure to ELF-MF emissions from UCLs. The ELF-MF emissions from the 154 kV UCL were 15.4±24.4 (GM: 7.8)mG, while from the 345 kV line they were 6.0±2.4 (GM: 5.7)mG. Through the comparison between ELF-MF emissions of 154 kV UCL and HVTL, at about 20 m distance from an overhead line the emissions level is 4 mG, while from an underground line at about 10 m distance the emission level was recorded as less than 4 mG. Through comparing the ELF-MF emission amount of the UCL according to the burial method, it was found that the direct ELF-MF emission levels are 15.3±7.4 (GM: 13.9)mG at the direct point, in the conduit type 21.0±30.4 (GM: 10.8)mG, and in the buried form 8.5±12.3 (GM:5.1)mG. In this study, ELF-MF emissions were about 37.0% and 47.5% lower, respectively, compared with the direct power and conduit type. The correlation between ELF-MF emission (mG) and power load (A) was analyzed. The higher the power load, the higher the ELF-MF emission. The correlation between ELF-MF emission at the direct point and depth of the UCL was also analyzed, and it was found that as the depth of line burial increased, ELF-MF emissions decreased.

The purpose of this study is to investigate the level of ELF-MF emissions from underground cable lines near daycare centers in the metropolitan city of Seoul. We investigated 143 daycare centers from June to September of 2015. In addition, the rate of reduction of ELF-MF levels according to the distance from the line was calculated using simulations. The ELF-MF emission level of 143 daycare centers at boundary point was 1.37 ± 1.75 mG (GM: 0.75 mG) and at direct point was 11.14 ± 17.99 mG (GM:6.05 mG). ELF-MF levels at direct point were 8.13 (arithmetic mean) and 8.06 (geometric mean) times higher, respectively, than that at the boundary point. By analyzing the relationship between ELF-MF and electricity current (A) and operating depth (m), a significant correlation was found between ELF-MF and current (A) and depth (m), at 0.360 (p<0.01) and -0.303 (p<0.05), respectively. The results of the simulation showed that appropriate separation distances showing below 4 mG was 8m and 14m, adjusted mean current (A) and maximum current (A), respectively. The results of the study suggest that a plan should be implemented for the management of ELF-MF in High voltage power-line and Underground cable line areas, through a broad and detailed survey and risk communication.

In this study, ELF-MF levels of subway trains were measured to understand the status of the intensity of ELFMF. The measurement points for the train are selected in the center of each train compartment(pantagraph compartment, motor-driven compartment and the compartment that is not connected to any other electric equipment) using EMDEX II. ELF-MF levels of trains were measured from the starting to the terminal station in each lines(Seoul line 1-9, Incheon line 1, Incheon international airport line, Gyungui line, Bundang line, Gyeongchun line, Joongang line, Suin line). We found that the mean and range of ELF-MF levels in the DC power subway train are 2.4 and 0.1~125.9 mG, respectively, while the mean and range of ELF-MF levels in the AC power subway train are 10.4and 0.0~156.3 mG, respectively. Furthermore, the maximum ELF-MF level(156.3 mG) was lower than the reference level(ICNIRP 833 mG, 60Hz). The findings of this study in relation to the characteristics of ELF-MF for subway will be useful to derive the ELF-MF exposure coefficient from our living environment in a subsequent study.

The light trespass problem still has not been solved for a long time because of the complex influences of the reflection or overlap lights. To solve the light trespass problem, the assessment of the characteristics of the spilt light carry out firstly. In this study, we estimated the light trespass reducing performance of various load lightings using by RELUX lighting simulation program. In the simulation program, we designed the lighting environment according to the streetlight installation guideline by the ministry of land, transport and maritime affairs. And we estimated the light trespass caused by roadway lighting from first floor position to fourth floor position. And we compare the light trespass caused by back light of the roadway lighting with the light trespass caused by forward light. Then we estimated the effect of light trespass by improving the light distribution of roadway lighting from Backlight rating 3 to Backlight rating zero. From the research, we find that the light trespass caused by roadway lighting maximize at the first floor position of the house. And the light trespass contribution rate by backlight and forward light is 66 percentage and 33 percentage respectively. And we estimated that the light trespass can be decreased about 40 % by improving the backlight. The result derived from this research will be helpful to establish the light pollution reduction plan to minimize the adverse effect by the spilt light from the roadway lighting.

Chromated Copper Arsenate (CCA)-treated wood has been widely used in Korea since 1980s, but the release of chromium, copper, and arsenic from the wood has been reported to cause environmental contamination. This study was aimed at investigating the environmental impact of brook water and sediment from the construction of cylindrical wood piles around a brook (partially immersed in the water) and wood bridge structures over the brook. Ten water and ten composite sediment samples (including one control for each) were collected from sites where a large number of treated wood structures were installed. Samples were analyzed for total chromium, copper, and arsenic using atomic absorption spectroscopy. Water contamination was not observed in all samples, but metal concentrations in the sediment samples were elevated at most sites, indicating the accumulation of metals in the sediment. This study suggested that the use of CCA-treated wood by continuos contact with water can lead to marked leaching of metal components and may ultimately cause health effects on aquatic organisms living on or in the sediment.