• Title/Summary/Keyword: heavy metal distribution

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A Study on the Property and Performance Characteristics of Different Kind Engine Oil by Endurance Test of Heavy-duty Diesel Engine (대형 디젤엔진 내구 시험에 의한 다른 종류 엔진오일의 물성 및 성능 특성에 관한 연구)

  • Lee, Minho;Kim, Jeonghwan;Song, Hoyoung;Kim, Giho;Ha, Jonghan
    • Transactions of the Korean Society of Automotive Engineers
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    • v.22 no.7
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    • pp.48-56
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    • 2014
  • Engine oil is an oil used for lubrication of various internal combustion engines. The main function is to reduce wear on moving parts; it also cleans, inhibits corrosion, improves sealing, and cools the engine by carrying heat away from moving parts. In engines, there are parts which move against each other. Otherwise, the friction wastes the useful power by converting the kinetic energy to heat. Those parts were worn away, which could lead to lower efficiency and degradation of the engine. It increases fuel consumption, decreases power output, and can induce the engine failure. This study was conducted to evaluate the relation between engine oil property changes and engine performance for the diesel engine. This test was performed by using 12L, 6 cylinder, heavy duty engines. Low SAPS 10W30 engine oil (two type engine oils) was used. Test procedure and method was in accordance with the modified CEC L-57-T97 (OM441LA) method. In this study, TAN, TBN, KV and metal components, engine power, blowby gas, A_F were presented to evaluate the relation with engine oil property changes and engine performance. TAN, TBN, KV and metal We found that the components were generally increased but engine performance did not change. This results mean that property changes did not affect on engine performance because those were not enough to affect engine performance.

Distribution of Heavy metals in Soil at Iksan 1st Industrial Complex Area (익산 제 1 공단 토양의 중금속 함량 분포 조사)

  • Kim, Seong-Jo;Baek, Seung-Hwa;Moon, Kwang-Hyun;Jang, Kwang-Ho;Kim, Su-Jin
    • Korean Journal of Environmental Agriculture
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    • v.17 no.1
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    • pp.48-53
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    • 1998
  • The purpose of this study was to compare heavy metal concentrations in uncontaminated soil with those in soil influenced by industrial activities, and to investigate the relationship between change of heavy metal content and the kind of industry at the Iksan 1st Industrial Complex that has started since 1975. Soils sampled in 0-3㎝ and 3-6㎝ soil depth, respectively were analized for content of Cd, Cu, Ni, Pb and Zn. Change of heavy metal content in soil of the industrial complex were more accumulated 16 to 25% of Cd and Cu, 93% of Pb and Zn, respectively in samples compared with natural soil uncontaminated. But there was no different in Ni content between two soil. Distribution of Cd in soil layer of 0 to 3cm was the highest concentration of 5 ppm more at the textile industries, and then higher at the chemicals and the food processing industries. In 3 to 6㎝ soil layer Cd content was the highest concentration of 5 ppm more at the metal processing industries, and then higher at the textile industries. Cd accumulation in soil was different according to a kind of industry and soil depth. Cu content was the highest value of 400 ppm more in soil layer of 0 to 3cm at the manufacturing electric wires industry area and showed the accumulation phenomenon in soil layer 3 to 6cm at the ohmmeter, machines and electric wires industry area. Ni content was 35 ppm more in soil of the metal plating and processing industries regardless of soil sampling layer. Then it was 25 ppm more in soil of the building stones and semiconductor industries. Pb content was from 400 to 1000 ppm in soil of the chemicals and textiles industries regardless of soil sampling layer. Zn content was 1200 ppm more in soil of the chemicals and silk fabrics industries regardless of soil depth, and then lower in order to soil of leather processing${\le}$metal plating industries. In conclusion, changes of heavy metal kinds and content in soil of this industrial complex area were caused by the type or kinds of industrial activities. Changes of Pb and Zn content in soil were dominated at this area.

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Interpretation of heavy metal elements from the road dusts using GIS (GIS를 이용한 도로 분진의 중금속원소 함량 해석에 관한 연구)

  • 이효재;이근상;이언호;장영률
    • Spatial Information Research
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    • v.10 no.2
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    • pp.201-213
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    • 2002
  • Chemical analyzes were carried out the samples from roadsides of the Gwangju city. The purpose of this research is to investigate the concentrations and distribution patterns of heavy metals due to urbanization and industrialization in the Gwangju city This study area is not significantly contaminated based on the concentrations of Cd, Cu, Fe, Mn, Pb and Zn. However, the concentrations of the chemical elements analyzed are locally higher than those of serious contamination level indicated by Ministry of environment. The dust pH is in the rage of 5.60-7.09 and was generally neutral, and there are no difference in pollution area and nonpollution area. Chemical analyses utilized are dilution by 0.1N HCl. In result of analysis by the method using 0.1N HCl, concentrations of Cd and Cu are a little high in Gwangchondong of Seo-Gu. Concentrations of Mn and Pb are a little high in Buk-Gu and Nam-gu, and Concentrations of Zn are generally higher than average of soils. Zn, in the study area, keeps polluting greatly as Zn concentration of average is 150.9ppm. All of P.I values are lower than 1, it means heavy metal pollution is not serious.

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Comparison of properties and heavy metal contents of paddy and Jeju rices (재배방식이 다른 논쌀과 제주밭쌀의 특성 및 중금속 함량비교)

  • Lee, Seung-Woo;Han, Jung-Ah
    • Korean Journal of Food Science and Technology
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    • v.50 no.2
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    • pp.138-142
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    • 2018
  • The physical properties and heavy metal content in rices that were grown in different conditions were compared; two paddy rices grown in irrigated water and a Jeju rice grown in dry field without irrigation. The pasting properties, color, or amylopectin chain length distribution were different, however, they were independent of growing conditions. For heavy metals such as Pb or Cd, Jeju rice showed similar content to paddy rices. However, total and inorganic arsenic (As) contents were much lower; for Jeju rice, the total arsenic content was only 10.1-17.9% of that in two paddy rices, and the inorganic arsenic was just corresponding to 15% of that in paddy rice. The inorganic arsenic content decreased by 34.1, 23.8, and 17.5% in paddy rice by soaking, cooking, and dripping with hot water, respectively.

Geochemical Study of Coastal Sediments around the Samcheonpo Coal-fired Power Plant (삼천포화력발전소 주변해역 퇴적물의 지구화학적 연구)

  • Lee, Doo-Ho;Lim, Ju-Hwan;Jeong, Yeon-Tae;Jeong, Nyeon-Ho;Kang, Jeong-Won
    • Journal of Environmental Impact Assessment
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    • v.10 no.2
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    • pp.85-98
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    • 2001
  • This study was conducted to investigate the geochemical factors governing the distribution of heavy metals(Co, Cr, Cu, Fe, Mn, Ni, Pb, and Zn) in the marine surface sediment samples collected from the Samcheonpo coal-fired power plant. Variations of absolute metal concentrations were related to those in textural and/or carbonate and organic matter content. Most elements, except for Pb, showed generally lower contents compared with the average shale concentration, and the effect of anthropogenic input appeared to be minimal in the sediments. Computations of LF%(labile fraction) and EF(enrichment factor) based on all trace metal data indicated the presence of mineralogical control for Co, Cr, Cu, Ni, and Zn, and anthropogenic contamination for Pb, which needs to be considered in the design of long term monitoring programmes.

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The Extraction Characteristics of Metal-contaminated Soil by Soil Washing (토양세척기법을 이용한 중금속 오염토양 처리에서 중금속 추출특성)

  • Hwang, Seon-Suk;Lee, Noh-Sup;NamKoong, Wan
    • Journal of Korean Society of Environmental Engineers
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    • v.27 no.10
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    • pp.1072-1080
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    • 2005
  • The extraction characteristics of heavy metals(HM) from a contaminated soil at existing lead smelters were investigated with ethylene diamine tetraacetic acid(EDTA), citrate and HCl as washing solutions. EDTA was more effective for Pb than for other heavy metals. As the mol ratio of EDTA/HM increased, the removal efficiency of heavy metals became higher. When the mol ratio of EDTA/HM approached to 6.5, it removed Pb most effectively. Citrate was effective especially in extracting Zn. The removal efficiency of HCl was comparatively high in almost all heavy metals, and at 0.3N concentration it was the highest. After soil washing process by the use of EDTA, the great part of exchangeable fractions and most of heavy metals of weakly adsorbed like carbonate fraction were extracted. For washing with citrate and HCl, four heavy metals showed the similar exchange of chemical partitioning and the exchangeable fractions of Pb which has weakly adsorbed to soil were more increased than before the process. As removal efficiency of citrate washing process depends upon the distribution of non-detrital fractions, so it can be contended that only the amount of non-detrital fractions could be removed from all the heavy metal content. EDTA and HCl could remove most of non-residual fractions in all heavy metals except Zn. As a result of EDTA washing, toxicity characteristic leaching procedure(TCLP) concentration of the processed soil met the USEPA Pb limit of 5.0 mg/L.

A Study on the Horizontal and Vertical Distribution of Heavy Metal Elements in Slime Dump from Dukum Mines, Korea (덕음광산 선광광미와 주변토양의 중금속에 대한 수평.수직적인 분산에 관한 연구)

  • 박영석
    • Economic and Environmental Geology
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    • v.33 no.2
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    • pp.91-100
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    • 2000
  • It has been more than ten years since Dukun mine was abandoned. Tailings of waste deposits and slime dumps in the abandoned Dukum mine have been left to be deserted for fifty years. The results of fifty years of neglecting are nothing short of major environmental problems. Slime dumps have been exposed to air and water in the mine over ten years and then soil profile has been formed well. Soil in the upper layer (A horizon) is the light gray color due to the leaching of cations. Soil in the lower layer (A2 horizon, 0.2∼0.3m)is tinted with reddish brown and yellowish brown color due to the development of iron oxides and iron hydroxides. Soil in the lower part of B horizon of (1.0∼3.0m) with the growth of copper and zinc oxides exposes to the bluish green, light blue, and dark gray. Ranging from 3m to 8m in depth, 85 samples were taken from 22 sampling sites with 50m intervals located on the slime dump area with hand auger and trench (open cut). As tailings was distributed, heavy metal elements extracted by the process of surface water and ground water move and disperse in to the hydrosphere. Waste dumps were distributed in and around the mine and water draining from those dumps be a potential source of contamination. Soils, thus, can be dispersed into downslope and downstream through wind and water by clastic movement. These materials may be deposited in another horizon if the water is withdrawn, or if the materials are precipitated as a result of differences in pH, or other conditions in deeper horizons. These were primarily associated with acid mine drainage. The characteristics and rate of release of acid mine drainage are influenced by various chemical and biological reactions at the source of acid generations. Prolonged extration of heavy metal elements has a detrimental effect on the agricultural land and residental area. Twenty soil samples were collected from the agricultural land in the area (0∼30 cm). Seventeen samples were also taken from the sediment in the stream running alongside the dumps. The dispersion patterns of heavy metal elements are as follows: The content of As ranged 2∼6 ppm in a horizon, 20∼125 ppm in B horizon with large amount of clay mineral is concentrated and the content of Cd ranged 1∼2 ppm in A horizon, 4∼22 ppm in B horizon. Like Cd, the content of As, Cu, Zn, Pb in B horizon is higher than that in A horizon (approximately 5∼100 times). When soil formation proceeds in stages, it is necessary to investicate the B horizon with the concentration of heavy metal and preventive measures will have to established.

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Heavy Metal Contents in Upland Soils and Crops of Korea (우리나라 밭 토양 및 작물의 중금속함량)

  • Jung, Goo-Bok;Kim, Ho-Chung;Jung, Ki-Yeol;Jung, Beung-Kan;Kim, Won-Il
    • Korean Journal of Soil Science and Fertilizer
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    • v.31 no.3
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    • pp.225-232
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    • 1998
  • In order to monitor the degree of heavy metal distribution in upland cultivations in Korea, both the cultivated soils and crops were collected from the 854 and 140 sites, respectively. The contents of cadmium (Cd), copper(Cu), lead(Pb), and zinc(Zn) in each sample were measured by Inductively Coupled Plasma(ICP) technique after 1N-HCl extraction. The content of Arsenic(As) was also measured with the same technique after 1N-HCl extraction. The average contents of heavy metal in surface soils(0~15 cm depth) were $0.135mg\;kg^{-1}$ for Cd, $2.77mg\;kg^{-1}$ for Cu, $3.47mg\;kg^{-1}$ for Pb, $10.7mg\;kg^{-1}$ for Zn, and $0.57mg\;kg^{-1}$ for As. Heavy metal contents of soil were similar to those values measured for upland soils in 1989, lower than soils under plastic film house in 1996. However, these contents were lower than "Countermeasure values for soil contamination"(Cd: 4, Cu: 125, Pb: 300, and As: $15mg\;kg^{-1}$ in soil) describled in Soil Environmental Conservation Act in Korea(1996). The contents of heavy metal in fresh vegetable, and root and tuber crops ranged $0.005{\sim}0.019mg\;kg^{-1}$ for Cd, $0.20{\sim}1.03mg\;kg^{-1}$ for Cu, $0.042{\sim}0.104mg\;kg^{-1}$ for Pb, and $2.0{\sim}4.0mg\;kg^{-1}$ for Zn, respectively.

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Distribution of $NO_3\;^-,\;SO_4\;^{2-}$ and Heavy Metals in Some Urban-forest Soils of Central Korea (중부 지역 도시 자연녹지 토양중 $NO_3\;^-,\;SO_4\;^{2-}$ 및 중금속 분포)

  • Kim, Kye-Hoon;Park, Soon-Nam
    • Korean Journal of Environmental Agriculture
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    • v.19 no.4
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    • pp.351-357
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    • 2000
  • This study was carried out to find out characteristics and contamination status of the urban-forest soils. Both topsoil (0-20 cm) and subsoil (40-60 cm) samples were collected from Namsan, Changdeok-palace, Seongjusan and Odaesan (control). The samples were analyzed for physicochemical properties, heavy metal (Cd, Cu, Pb, Zn) and anion $(NO_3\;^-,\;SO_4\;^{2-})$ contents. Soil pH of Odaesan was the highest followed by Namsan, Changdeok-palace and Seongjusan. The anion concentrations of the soil samples were in the order of Namsan, Seongjusan > Changdeok-palace > Odaesan. The relationships between soil pH and the anion concentrations showed highly significant negative correlation, which indicated acidification of soil due to air pollutants such as $NO_3\;^-$ and $SO_4\;^{2-}$ was going on. The heavy metal contents of the soils of urban-forest were higher than those of control. Heavy metal contents in the topsoil were higher than those in the subsoil. Since urban-forest soils were quite vulnerable to acidification and heavy metal accumulation due to chronic exposure to air pollutants such as automobile exhaust, a comprehensive countermeasure not to deteriorate urban-forest ecology must be prepared in the near future.

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Geochemical transport and water-sediment partitioning of heavy metals in acid mine drainage, Kwangyang Au-Ag mine area, Korea

  • Jung, Hun-Bok;Yun, Seong-Taek;Kwon, Jang-Soon;Lee, Pyeong-Koo
    • Proceedings of the Korean Society of Soil and Groundwater Environment Conference
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    • 2003.09a
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    • pp.409-412
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    • 2003
  • Total extraction of stream sediments in the Kwangyang mine area shows their significant pollution with most trace metals such as Cr, Co, Fe, Pb, Cu, Ni, Zn and Cd, due to sulfide oxidation in waste dumps. Calculations of enrichment factor shows that Chonam-ri creek sediments are more severely contaminated than Sagok-ri sediments. Using the weak acid (0.1N HCl) extraction and sequential extraction techniques, the transport and sediment-water partitioning of heavy metals in mine drainage were examined for contaminated sediments in the Chonam-ri and Sagok-ri creeks of the Kwangyang Au-Ag mine area. Calculated distribution coefficient (Kd) generally decreases in the order of Pb $\geq$Al > Cu > Mn > Zn > Co > Ni $\geq$ Cd. Sequential extraction of Chonam-ri creek sediments shows that among non-residual fractions the Fe-Mn oxide fraction is most abundant for most of the metals. This indicates that precipitation of Fe hydroxides plays an important role in regulating heavy metal concentrations in water, as shown by field observations.

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