• 해양환경안전학회지
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• 제21권3호
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• pp.223-233
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• 2015

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.

• 자원환경지질
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• 제42권2호
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• pp.121-131
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• 2009

폐기물 해양 투기 지역인 동해병과 서해병 해역 표층퇴적물의 입도, 광물학적 특성, 퇴적속도 및 중금속 함량을 분석하여 중금속 분포 특성을 비교하였다. 동해병과 서해병 해역의 입도는 각각 $7.95{\sim}8.51{\Phi}$와 $7.42{\sim}8.15{\Phi}$의 범위이며, 동해병 해역의 일부 정점을 제외한 모든 정점의 퇴적상은 니질 퇴적물에 속한다 연구지역 표층퇴적물의 주 구성 점토광물은 일라이트이며, 카올린 계열 광물과 녹니석, 스멕타이트로 소량 구성되어 있다. $^{210}Pb$에 의해 추정된 동해병해역 표층퇴적물의 퇴적속도는 1.11 mm/yr$\sim$1.73 mm/yr이며, 서해병해역 퇴적물의 퇴적속도는 1.87 mm/yr이다. 상관성 분석 결과, 니켈, 구리, 크롬 및 아연은 평균입도, 알루미늄 및 철과 밀접한 상관성을 보인다. 반면, 연구지역 퇴적물의 카드뮴과 납은 이들 요소들과 상관성이 결여되어 있을 뿐만 아니라, 부화지수가 1.5이상으로 인위적인 오염의 징후를 보인다. 그리고 카드뮴과 납의 $I_{geo}$-class 역시 대부분 $2{\sim}4$로 moderately polluted$\sim$strongly polluted로 분류된다. 특히, 동해병의 $I_{geo}$-class가 최대 4인 strongly polluted로 분류되어 서해병 해역보다 높다. 이는 동해병 해역에 투기되는 폐기물이 서해병 해역에 투기되는 폐기물뿐만 아니라, 광물성폐기물, 하수도준설토사, 건설공사 오니 등이 추가로 배출되고 있으며, 양적으로도 서해병 보다 두 배 이상 투여되기 때문인 것으로 판단된다.

• 한국식품영양과학회지
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• 제38권4호
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• pp.517-524
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• 2009

본 연구에서는 2003년부터 2004년까지 동해, 서해 및 남해 연안에서 채취하여 위판장에서 판매되고 있는 연안산 어류총 53종 177개체에 대한 중금속 함량을 분석하였다. 인증표준물질(certified reference material, CRM)을 사용한 각 중금속에 대한 회수율은 평균 $88.7{\sim}100.6%$로 Codex에서 요구하고 있는 수준에 부합하였다. 어류의 중금속 함량(생물기준)은 아연이 $8.981{\pm}4.835{\mu}g/g$으로 가장 높았으며, 다음으로, 구리 $0.755{\pm}0.507{\mu}g/g$, 망간 $0.433{\pm}0.699{\mu}g/g$, 크롬 $0.206{\pm}0.181{\mu}g/g$, 니켈 $0.081{\pm}0.110{\mu}g/g$, 납 $0.038{\pm}0.046{\mu}g/g$, 카드뮴 $0.017{\pm}0.023{\mu}g/g$ 순이었다. 한편, 우리나라 국민의 어류를 통한 중금속의 1일 섭취량은 각각 카드뮴 0.81 ${\mu}g$, 크롬 9.98 ${\mu}g$, 구리 36.63 ${\mu}g$, 망간 21.01 ${\mu}g$, 니켈 3.93 ${\mu}g$, 납 1.84 ${\mu}g$ 및 아연 435.58 ${\mu}g$이었다. 이는 FAO/WHO에서 설정한 잠정주간섭취허용량인 PTWI와 비교해 보면, 카드뮴 1.35%, 구리 0.12%, 납 0.86% 및 아연 0.73% 수준이었다. 따라서 우리국민이 어류를 통해 일주일에 섭취 하는 카드뮴 및 납의 함량은 PTWI의 $0.86{\pm}1.35%$에 해당되며, 이들 유해 중금속 함량은 매우 안전한 수준인 것으로 판단된다.

• 한국산림과학회지
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• 제84권3호
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• pp.286-298
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• 1995

본 연구는 산림토양(山林土壤)의 산성화(酸性化)가 토양내 치환성 양이온($Ca^{2+}$, $Mg^{2+}$, $Al^{3+}$) 및 중금속(Cu, Zn, Mn, Pb, Cd) 분포(分布)에 미치는 영향을 평가하고, 이러한 토양내 화학적 특성과 임목의 세근과 엽내 양료 및 중금속 분포와의 관계(關係)를 파악하기 위하여 수행되었다. 이를 위하여 울산(蔚山)과 온산공단(溫山工團) 주변의 6개 조사구와 개발제한지역내(開發制限地域內) 2개 조사구를 대상으로 토양 pH의 장기적(長期的) 변화(變化)와 토양(土壤), 세근(細根) 및 엽(葉)내 양료(養料)와 중금속(重金屬) 함량(含量)을 조사한 결과는 다음과 같다. 1. 울산지역 산림의 토양 pH(A층)는 1987년에 활엽수림(闊葉樹林)과 침엽수림(針葉樹林)에서 각각 4.45와 4.78이었던 것이 1994년에는 각각 3.73과 3.86으로 감소하여 토양산성화(土壤酸性化)의 정도가 심화되었다. 1994 년 현재 개발제한지역내 침엽수림인 동천이 4.57로 가장 높은 반면 온산공단에 인접한 당월의 활엽수림이 3.19로 가장 낮았다. 2. 공단지역(工團地域)에 비해 토양 pH가 높았던 개발제한지역 산림의 토양내 치환성(置換性) $Ca^{2+}$함량은 공단지역보다 활엽수림에서 3.5배, 침엽수림에서 11배나 높았고, 치환성(置換性) $Mg^{2+}$ 함량 또한 각각 4.5배와 5배나 높았다. 그러나 공단지역에서 높을 것으로 예상되었던 치환성(置換性) $Al^{3+}$함량은 오히려 개발제한지역에서 높게 나타났다. 3. 세근내(細根內) Ca과 Mg 함량은 개발제한지역이 공단지역보다 활엽수(물오리나무, 상수리나무)의 경우 각각 3.6배와 1.7배 높았고 침엽수(리기다소나무, 곰솔)에서는 각각 4.6배와 1.5배 높았다. 엽(葉)에 있어서도 개발제한지역 산림의 활엽수가 공단지역보다 각각 1.1배와 2.2배 높았고, 침엽수는 각각 1.8배와 2.3배나 높았다. 그리고 세근과 엽내 Al 함량 역시 토양에서와 같은 경향을 보였다. 4. 토양산성화도(土壤酸性化度)와 임목(林木)에 대한 Al 독성(毒性)을 평가하기 위한 토양과 세근내 Ca/Al 몰비가 동천을 제외한 오든 조사구의 토양과 세근에서 1 이하로써 토양산성화에 민감할 뿐만 아니라 양료흡수(養料吸收) 및 근계발달(根系發達)의 피해(被害)가 예상되었다. 침엽수림(針藥樹林)의 경우 토양 pH와 토양 및 세근내 Ca/Al 몰비간에 서로 고도(高度)의 상관(相關)을 보였다. 5. 토양, 세근 및 엽내 Cu, Zn, Pb 함량은 활 침엽수림 모두에서 공단지역(工團地域)이 개발제한지역(開發制限地域)보다 전체적으로 높았지만, 토양중 Mn과 Cd 함량은 반대로 개발제한지역이 더 높았다.

• 한국산업보건학회지
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• 제9권1호
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• pp.56-72
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• 1999

Airborne concentrations of welding fumes in which 13 different metals such as Al, Cd, Cr, Cu, Fe, Mn, Mo, Ni, Pb, Si, Sn, Ti, and Zn were analyzed were measured at 18 factories including automobile assembly and manufactures, steel heavy industries and shipyards. Air samples were collected by personal sampler at each worker's worksite(n=339). Blood levels of Cd, Cu, Fe, Mn, Pb and Zn were also measured from samples taken from 447 welders by atomic absorption spectrometry and compared with control values obtained from 127 non-exposed workers. The results were as follows ; 1. Among various welding types, $CO_2$ welding 70.2 % were widely used, shielded metal arc welding(SMAW) 22.1 % came next, and rest of them were metal inert gas(MIG) welding, submerged arc welding(SAW), spot welding(SPOT) and tungsten inert gas(TIG) welding. 2. Welding fume concentration was $0.92mg/m^3$($0.02{\sim}15.33mg/m^3$) at automobile assembly and manufactures, $4.10mg/m^3$($0.02{\sim}70.75mg/m^3$) at steel heavy industries and $5.59mg/m^3$($0.30{\sim}91.16mg/m^3$) at shipyards, respectively, showing significant difference among industry types. Workers exposed to high concentration of welding fumes above Korean Permissible Exposure Limit(KPEL) amounted to 7.9 % and 12.5 %, in $CO_2$ welding and in SMAW at automobile assembly and manufactures and 62.7 % in $CO_2$ welding, and 12.5 % in SMAW at shipyards, and 66.2 % in $CO_2$ welding and 70.6 % in SMAW at steel heavy industries. 3. Geometric mean of airborne concentration of each metal released from welding fumes was below one 10th of KPEL in all welding types. Percentage of workers, however, exposed to airborne concentration of metals above KPEL amounted to 16.8 % in Mn and 7.6 % in Fe in $CO_2$ welding; 37.5 % in Cu in SAW, 30 % in Cu in TIG; and 25 % in Pb in SPOT welding. As a whole, 76 Workers(22.4%) were exposed to high concentration of any of the metals above KPEL. 4. There were differences in airborne concentration of metals such as Al, Cd, Cr, Cu. Fe. Mn, Mo, Ni, Pb, Si, Sn, Ti and Zn by industry types. These concentrations were higher in shipyards and steel heavy industries than in automobile assembly and manufactures. Workers exposed to higher concentration of Pb above KPEI amounted to 7.4 % of workers(7/94) in automobile assembly and manufactures. In shipyards, 19.2 % of workers(19/99) were over-exposed to Mn and 7.1 % (7/99) to Fe above KPEL. In steel heavy industries, 14.4 %(21/146), 7.5 %(11/146) and 13 %(19/146) were over-exposed to Mn, Fe and Cu, respectively. As a whole, 76 out of 339 workers(22.4%) were exposed to any of the metals above KPEL. 5. Blood levels of Cd, Cu, Fe, Mn, Pb, and Zn in welders were $0.11{\mu}g/100m{\ell}$, $0.84{\mu}g/m{\ell}$, $424.4{\mu}g/m{\ell}$, $1.26{\mu}g/100m{\ell}$, $5.01{\mu}g/100m{\ell}$ and $5.68{\mu}g/m{\ell}$, respectively, in contrast to $0.09{\mu}g/100m{\ell}$, $0.70{\mu}g/m{\ell}$, $477.2{\mu}g/m{\ell}$, $0.73{\mu}g/100m{\ell}$, $3.14{\mu}g/100m{\ell}$ and $6.15{\mu}g/m{\ell}$ in non-exposed control groups, showing significantly higher values in welders but Fe and Zn.

• 대한두경부종양학회지
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• 제15권2호
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• pp.149-155
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• 1999

Objectives: To study the clinical features of the primary nasal/nasopharyngeal non-Hodgkin's lymphomas and to evaluate the implication of immunophenotyping as a prognostic factor. Patients and Methods: From January 1990 to December 1997,41 patients(median age, 41 years) of primary nasal/nasopharyngeal non-Hodgkin's lymphoma were studied. The clinical records and paraffin-embedded tissue blocks were reviewed retrospectively. The histologic features, immunophenotypic findings(pan-T, pan-B, CD3, CD56) and Epstein-Barr virus in situ hybridizatios were examined. The prognostic factors for clinical outcome were evaluated in these patients. According to Ann-Arbor system, there were 30 patiets(73%) with stage IE, 4(10%) with stage IIE, 3(7%) with stage IIIE, 4(10%) with stage IVE lymphoma. Among the patients with stage IE/IIE, 4 patients received local radiation alone, 4 received chemotherapy alone, 25 received combination chemotherapy and radiotherapy and 1 refused treatment. The patients with stage IIIE/IVE were given combination chemotherapy and radiotherapy. Results: Immunophenotyping were performed in 40 patients and staining results were as follows: 3(7%) patients with B cell, 17(42%) with T cell, 18(44%) with NK/T cell(CD56 positive), and two patients with unclassifiable result. Epstein-Barr(EB) virus in situ hybridization were performed in 28 patients and 23(82%) patients had positive EBV-encoded RNAs(EBERs). 21(55%) patients achieved a complete remission. There was no difference in complete remission between radiation alone and combination therapy. With median follow-up of 30 months, 5-years disease free survival of complete responders was 60% and 5-years overall survival rate was 36%. Multivariate analysis showed that better overall survival was related with absence of B symptoms, ECOG performance${\leq}1$ and non-NK cells. Conclusion: Most of all cases were positive for EBER. Since NK/T phenotype carried the worst prognosis, analysis for CD56 expression should be done. Further prospective studies were warranted to evaluate the role of chemotherapy in stage IE/IIE.

• 한국환경보건학회지
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• 제43권3호
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• pp.233-239
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• 2017

Objectives: The pollution status of heavy metals within the soil was investigated with an aim to establishing a sustainable soil environment within parks and amusement facilities installed in urban areas of Gyeonggi-do Province. Methods: As sampling sites, 14 locations were selected from a city with a number of factories near a residential area, a residential area, and a children's park in a city with mixed green areas. Seven kinds of heavy metals, including Cd, Pb, and Hg, and the pH of soil were analyzed three times by inductively coupled plasma optical emission spectroscopy (ICP-OES) and atomic absorption spectrometer (AAS). Results: In this study, the pH of the samples from the residential park and industrial park showed 5.7-6.5 and 5.9-7.0, respectively. The overall mean concentration (mg/kg) of heavy metals was Zn (132.8), Ni (73.0), Cu (47.4), Pb (35.9), As (4.84), Cd (0.39), and Hg (0.07), indicating that these concentrations of heavy metals were lower than those for the area 1 standard of soil pollution concern criteria. In addition, the sampling sites in the residential area and the industrial area also showed the same tendency for concentration distribution. Conclusions: We found that the soil pollution class (SPC) of some spots were over 200, which are third and fourth classes. In order to manage a sustainable soil environment in a city park, it is suggested that local governments, the management bodies for these parks, need to manage, supervise, and investigate soil pollution and quickly replace contaminated soil.

• 한국환경과학회지
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• 제17권3호
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• pp.287-296
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• 2008

A comprehensive quality survey for heavy metals, organophosphorous and organochlorine residual pesticides, and coplanar PCBs in samples such as water, sediments and soils as well as spiders has been implemented. The samples were undertaken at nine stream sites and their vicinity in August 2006, representing different surrounding environments. The levels of PCBs were expressed as concentrations and WHO-TEFs. Among 12 coplanar PCBs as target compounds in this study, 2,3', 4,4', 5-PentaCB (IUPAC # 118) was the congener with the highest concentration. The total concentrations and TEF values of coplanar PCBs in Siheung stream sediment (heavy industrial complex site located in Ansan city) were 3915.50 pg/g and 0.8366 pg-TEQ/g on a dry weight basis, respectively. Such levels were around 40 times higher compared to sediment from Gapyung stream (green site located in the upper of Myunggi mountain). It is probably due to the direct input of PCBs trom PCBs treatment materials. Organophosphorous (EPN, dementon-s-methyl, diazinon, parathion, and phenthoate) and organochlorine (alpha-BHC, aldrin, 4,4'-DDT, 4,4'-DDE, endosulfan alpha and etc.) pesticides were not detected above 5 ppb of detection limits. The concentrations of Cu and Cd in water and sediment samples from Siheung stream were 44.11 and $0.17ug/m\ell$ and $713.42{\mu}g/g$ and $3.73{\mu}g/g$, respectively, which contained $20\sim40$ times higher concentrations than those from Gapyung stream. In addition to the water and sediment samples, the levels of heavy metals in spider from designated sampling sites were also determined. Heavy metals in spider collected near Siheung stream was appeared to be equivalent and/or a little higher levels with respect to other spiders. Furthermore, the ratio of relative heavy metals (Cu, Cd, and Pb) in spider from each stream site showed a correlation as similar as that of heavy metals in soil samples.

• 한국진공학회:학술대회논문집
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• 한국진공학회 2014년도 제46회 동계 정기학술대회 초록집
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• pp.443-443
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• 2014

CIS 박막을 제조하기 위한 방법으로 셀렌화(selenization)방식, MOCVD방식, 동시진공증발(co-evaporation)방식, 전착(electrodeposition)방식 등이 있으나, 이러한 방식을 이용하여 CuInSe2 박막을 제조하는 경우 어떤 방법으로든 다원화합물의 조성 및 결정성을 조절하기가 매우 어려운 단점이 있었다. 기판의 온도를 일정 온도로 유지하도록 하고, 증발원을 가열하여 이에 내포된 물질(이원화합물 또는 단일원소)을 증발시켜 기판에 증착이 이루어지도록 하거나, 기판의 온도를 승온시키고 구리 이원화합물을 내포한 증발원을 가열해 물질을 증발시켜 기판에 증착이 이루어지도록 하는 방법으로 기판에 박막이 형성되도록 한다. 기판의 대면적화로 인해 균일한 박막의 형성이 어려워지고 있으며, 이중 15% 이상의 고효율을 보인 방법은 3-stage process를 이용한 동시진공증발방식으로, Cu, In, Ga, Se 등의 각 원소를 동시에 진공 증발시키면서 조성을 조절하여 태양전지에 적절한 전기적, 광학적 특성을 가지는 Cu(In,Ga)Se2 (CIGS)박막을 증착시키는 방법이다. 일반적으로, 실험실에서 연구되고 있는 장비의 구조는 증발원이 아래에 장착되어서 상향 증착되는 방식이다. 본 연구에서 사용된 장비는 하향 증발원이 측면에 장착되어서 하향 증착되는 방식으로 구성하였다. 증착되는 면방향으로, 적외선온도계(pyrometer)가 설치된 시창(viewport)의 오염 등으로 인하여, 지속적인 공정이 이루어지기 힘든 점을 개선하여 증착기판의 후면에 적외선 온도계를 설치하여 기판의 온도변화를 감지하여 공정에 반영할 수 있도록 하였다. 본 연구에서는 하향식 진공 증발원, 기판후면 온도모니터링모듈 등을 개발 장착하여, CIGS 박막을 제조하였으며, 버퍼층은 moving 스퍼터링법으로 ZnS를 증착하였고, 투명전극층은 PLD(Pulsed Laser Deposition)를 이용하여 제조하였다. 가장 높은 광변환효율을 보인 Al/ZnO/CdS/Mo/SLG박막시료는 유효면적 $0.45cm^2$에 광변환효율 15.65 %, Jsc : $33.59mA/cm^2$, Voc : 0.64 V, FF : 73.09 %를 얻을 수 있었으며, CdS를 ZnS로 대체한 Al/ZnO/ZnS/Mo/SLG박막시료는 유효면적 $0.45cm^2$에 광변환효율 12.45 %, Jsc : $33.62mA/cm^2$, Voc : 0.59 V, FF : 62.35 %를 얻을 수 있었다.

• 유기물자원화
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• 제11권2호
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• pp.66-73
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• 2003

석유화학공장폐수 슬러지를 폐석고와 시멘트, fly ash 및 고화제 등을 배합하여 성형하면 시멘트벽돌 및 보통시멘트의 압축강도 기준을 초과함으로 제조된 고화체는 벽돌, 블록, 경량골재, 노반재 등으로 활용이 가능할 것으로 판단되었다. 실험 결과 다음의 결과를 얻었다. 시멘트량을 전체 중량비의 20%인 1.29kg에서 fly ash/슬러지의 배합비의 모든 조건과 시멘트량을 전체 중량비의 15%인 0.9kg에서 fly ash/슬러지의 배합비가 0.31~0.45일 때, 시멘트벽돌 및 보통시멘트의 압축강도 기준을 초과하였다. 제조된 고화체(제품)의 유해성 평가를 위해서 침출수 중의 $Cr^{+6}$, Cu, Zn, Cd, Pb의 용출농도를 실시한 결과 모든 대상시료의 중금속 농도는 배출허용기준치 이내를 유지하여 유해물질로 인한 문제는 없을 것으로 판단되었다. 고화체를 시멘트벽돌 및 보통시멘트에 준해서 활용이 가능한 제조조건에서 제조원가를 조사하였다. 조사결과 자원화시설의 고화체 제조능력을 연간 약 18,000톤을 기준으로 할 때, 총괄원가 및 톤당제조원가는 각각 678,664천원 및 37,704원으로 조사되었다.