In order to evaluate the pollution of heavy metals in offshore surface sediments around shipyards in Korea, surface sediment samples were collected at eleven stations around four major shipyards located in the southeastern coast of Korea in summer 2010 and nine kinds of heavy metals such as copper(Cu), zinc(Zn), cadmium(Cd), lead(Pb), chrome(Cr), arsenic(As), mercury(Hg), iron(Fe) and aluminum(Al) in sediments were analyzed. The concentrations of Cu at all sampling stations were in the range of 47.10 ~ 414.96 mg/kg and exceeded TEL(Threshold Effects Level) 20.6 mg-Cu/kg of Korean marine environmental standards for offshore sediments and ERL(Effect Range-Low) 34.0 mg-Cu/kg . The concentrations of Cu at seven stations around four shipyards were 65.18 ~ 414.96 mg/kg and exceeded PEL(Probable Effects Level) 64.4 mg-Cu/kg of Korean marine environmental standards for offshore sediments. The concentration of Cu at one station around B-shipyard was 414.96 mg/kg and exceeded ERM(Effect Range-Median) 270.0 mg-Cu/kg . The concentrations of Zn at all stations were in the range of 135.09 ~ 388.79 mg/kg which exceeded ERL 150.0 mg-Zn/kg . The concentrations of Zn at seven stations around four shipyards were 157.57 ~ 388.79 mg/kg and exceeded PEL 157.0 mg-Zn/kg . The concentration of Zn at one station around B-shipyard was 388.79 mg/kg and was approaching ERM 410.0 mg-Zn/kg . The concentrations of Cd at all stations were in the range of 0.11 ~ 0.54 mg/kg and were below TEL 0.75 mg-Cd/kg and ERL 1.2 mg-Cd/kg . The concentrations of Pb at all stations were in the range of 18.04 ~ 105.62 mg/kg . The concentrations of Pb at two stations around B-shipyard were 73.87 ~ 105.62 mg/kg which exceeded TEL 44.0 mg-Pb/kg and ERL 46.7 mg-Pb/kg , and were below PEL 119.0 mg-Pb/kg and ERM 218.0 mg-Pb/kg . The concentrations of Cr at all stations were in the range of 51.26 ~ 85.39 mg/kg. The concentration of Cr at one station around B-shipyard was 85.39 mg/kg and exceeded ERL 81.0 mg-Cr/kg . The concentrations of As at all stations were in the range of 8.70 ~ 22.15 mg/kg which exceeded ERL 8.2 mg-As/kg and were below ERM 70.0 mg-As/kg . The concentrations of As at eight stations around A-shipyard, B-shipyard and D-shipyard were 14.93 ~ 22.15 mg/kg which exceeded TEL 14.5 mg-As/kg and were below PEL 75.5 mg-As/kg . The concentrations of Hg at all stations were in the range of 0.02 ~ 0.35 mg/kg. The concentrations of Hg at three stations around A-shipyard were 0.11 ~ 0.13 mg/kg which were almost equal to TEL 0.11 mg-Hg/kg . Those at two stations around B-shipyard were 0.27 ~ 0.35 mg/kg which exceeded TEL 0.11 mg-Hg/kg and ERL 0.15 mg-Hg/kg, and were below PEL 0.62 mg-Hg/kg and ERM 0.71 mg-Hg/kg. The concentrations of Fe and Al at all stations were in the range of 2.90 ~ 3.66 % and 3.12 ~ 6.80 %, respectively. These results imply that heavy metals such as copper, zinc, lead, arsenic and mercury were likely to be transferred to marine environment from shipyards, especially from B-shipyard.

국내 대형 조선소 주변해역의 중금속오염 현황을 밝히기 위하여 2010년 여름에 4개의 대형 조선소 주변 11개의 채수정점과 4개의 대조 정점에서 해수 시료를 채취하여 6종의 금속(Cu, Zn, Fe, Cd, Pb, Hg)을 분석하였다. 조선소별 주변해역 수중의 금속을 분석한 결과, (1) 구리(Cu)의 평균 농도는 0.817 ~ 1.638 ㎍/L로 해역환경기준(사람의 건강보호기준 20 ㎍/L, 해양생태계 보호 단기기준 3 ㎍/L)보다 낮았지만, 대조정점에 비하여 1.64 ~ 2.75배의 높은 값을 나타냈다. (2) 아연(Zn)의 평균 농도는 0.228 !~ 0.567 ㎍/L로 해역환경기준(사람의 건강보호기준 100 ㎍/L, 해양생태계 보호 단기기준 34 ㎍/L)보다 낮았지만, 대조정점에 비하여 1.62 ~ 5.91배의 높은 값을 나타냈다. (3) 철(Fe)의 평균 농도는 3.332 ~ 7.410 ㎍/L로 대조정점에 비하여 1.30 ~ 6.75배의 높은 값을 나타냈다. (4) 카드뮴(Cd)의 평균 농도는 0.013 ~ 0.028 ㎍/L로 해역환경기준(사람의 건강보호기준 10 ㎍/L, 해양생태계 보호 단기기준 19 ㎍/L)보다 낮았지만, 대조정점에 비해 1.18 ~ 2.33배의 높은 값을 나타냈다. (5) 납(Pb)의 평균 농도는 0.007 ~ 0.126 ㎍/L로 해역환경기준(사람의 건강보호기준 50 ㎍/L, 해양생태계 보호 단기기준 7.6 ㎍/L)보다 낮았다. (6) 수은(Hg)의 평균 농도는 0.002 ~ 0.004 ㎍/L로 해역환경기준(사람의 건강보호기준 0.5 ㎍/L, 해양생태계 보호 단기기준 1.8 ㎍/L)보다 낮았다. 비록 모든 중금속의 수중 농도가 해역환경기준보다 낮다고 할지라도, 선박 건조작업에 사용되는 구리, 아연, 철과 같은 중금속의 농도가 대조해역에 비해 조선소 주변해역에서 높다는 것은 조선소의 영향에 기인하는 것을 암시한다. 따라서 조선소로부터 각종 오염물질이 해양에 유입되지 않도록 통제하고 해양오염을 방지하는 국가적 차원의 해양환경관리가 필요하다.

Internal engine is the main power source of vehicle and is the main source of air pollution. To satisfy this getting rigorous emission regulation, it must be solved simultaneously the dilemma of reducing emission gas and increasing heat efficiency. Diesel engine is preferred compare with gasoline engine in aspect of energy consumption but it must be solved reducing the containing of NOx, CO and HC. In this study 1. Looking for alternative of performance improvement of Exhaust Gas Recirculation(EGR) which is emission gas reduction system, 2. Reducing malfunction of controlling emission gas 3. Made possible precision control

The high temperature due to climate change may result in the intensification of several drought and heat stress on crops including potato. These abiotic stress affect on potato development staages; sprout development, tuber initiation and maturation. Potatoes need moderate amounts of nitrogen and cool night for good tuber growth. Especially, high temperature in soil will delay tuber initiation and induce malformation. Therefore, to identify quickly heat tolerant lines and breeding potato lines adapt to high temperature in the field are needed. The objectives of this study were as follows; To apply in vitro screening method for identifying potato lines adapted to high temperature conditions. To verify these results under field assays carried out under natural high temperature field conditions. We used in vitro screening methods with breeding lines from Intranational Potato Center(CIP) under three temperature regime, 18℃, 25℃ and 30℃. All breeding liens had some genotype that produced microtubers at 18℃ and 25℃, with a clear tendency for lower percentage of tuberization at the high temperature. To verify in vitro screening methods for heat tolerance lines, we carried out natural high temperature filed evaluation at Tacna, La Molina and Sanramon in Peru. The results of both the in vitro test and the field assay showed clear relationship and similar expression of tuberization percentage. This finding supports the use of the in vitro assay as a rapid screening methods that represents performance at the field level. But the correlation between performance of the breeding lines under the in vitro and field condions was low. This could be due to differential response to breeding lines to characteristics of the field environment, such as soil salinity, drought, which were not represented in the in vitro assay.