• 한국환경보건학회지
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• 제49권6호
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• pp.324-333
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• 2023

Background: Human exposure to phthalates in indoor environments occurs via dermal absorption, oral ingestion of indoor dust, and inhalation of indoor air. However, systematic studies to investigate the exposure rate to phthalates among the three exposure routes in indoor environments are currently limited. Objectives: A theoretical exposure ratio between inhalation and oral exposure was calculated based on the total amount of di(2-ethyl-hexyl) phthalate (DEHP) emitted into indoor air and deposited into floor dust in a test house. Methods: Flooring and wallpaper containing DEHP were installed in a test house and the concentration of DEHP in both indoor air and floor dust were monitored for five months. Based on the measured DEHP concentrations, the theoretical total amount ratio of DEHP that could be exposed through inhalation and oral ingestion was calculated. Results: Considering the period of operation in the test house, the theoretical total amount of DEHP through inhalation and oral ingestion exposures in the entire test house space was calculated to be 0.014 mg and 5.5 mg, respectively. The exposure ratio of the two routes between inhalation and oral exposure corresponding to the total DEHP amount in flooring and wallpaper was 6.0×10^-7% and 2.3×10^-4%, indicating that theoretical oral exposure to DEHP is approximately 380 times higher than inhalation. Conclusions: Monitoring results from a test house has shown that oral exposure is the main exposure route for DEHP in indoor environments. The experimental design employed in this study and theoretical exposure ratio obtained can be applied to investigate actual exposure to DEHP and to determine the exposure characteristics of various types of semi-volatile organic compounds.

• 접착 및 계면
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• 제25권2호
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• pp.63-68
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• 2024

본 연구에서는 반도체 패키지용 와이어 본딩 공정에서 금(Au) wire의 표면처리에 적용되는 린스의 종류에 따른 Au wire의 오염 현상을 확인하고자 하였다. Au wire의 표면처리를 위해 실리콘(Si) 성분이 함유된 린스와 유기 계통으로만 이루어진 린스를 주로 사용하고 있으며, 실제 영향성을 확인하기 위해 두 종류의 1.0wt% 린스 용액으로 Au wire에 표면처리를 진행하였다. 이후, 반도체 공정에서 발생할 수 있는 Si 성분이 포함된 분진과의 반응성을 확인하기 위한 모사 실험을 진행하였다. 그 결과, optical microscopy(OM) 및 scanning electron microscopy(SEM) 분석을 통해 Si 성분이 함유된 린스로 표면처리한 Au wire의 경우 분진이 다량 흡착되었으며, 유기 계통으로만 이루어진 린스로 표면처리한 Au wire에는 소량의 분진이 흡착된 것을 확인하였다. 이는 Si 성분이 함유된 린스의 경우 상대적으로 극성을 띠기에, 주성분이 극성인 분진과 극성 상호작용을 일으키기 때문이다. 따라서 Si 성분이 존재하지 않는 린스를 사용하여 Au wire를 표면처리할 경우 분진에 의한 오염 현상이 감소하여 실제 와이어 본딩 공정에서 불량률을 낮추는 효과를 볼 수 있을 것으로 기대한다.

• 대기
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• 제27권1호
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• pp.41-54
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• 2017

Organic carbon (OC) and elemental carbon (EC) in $PM_{2.5}$ were measured using Sunset OC/EC Field Analyzer at Seoul Hwangsa Monitoring Center from March to April, 2016. The mean concentrations of OC and EC during the entire period were $4.4{\pm}2.0{\mu}gC\;m^{-3}$ and $1.4{\pm}0.6{\mu}gC\;m^{-3}$, respectively. OC/EC ratio was $3.4{\pm}1.0$. The average concentrations of $PM_{10}$ and $PM_{2.5}$ were $57.4{\pm}25.9$ and $39.7{\pm}19.8{\mu}g\;m^{-3}$, respectively, which were detected by an optical particle counter. The OC and EC peaks were observed in the morning, which were impacted by vehicle emission, however, their diurnal variations were not noticeable. This is determined to be contributed by the long-range transported OC or secondary formation via photochemical reaction by volatile organic compounds at afternoon. A conditional probability function (CPF) model was used to identify the local source of pollution. High concentrations of $PM_{10}$ and $PM_{2.5}$ were observed from the westerly wind, regardless of wind speed. When wind velocity was high, a mixing plume of dust and pollution during long-range transport from China in spring was observed. In contrast, pollution in low wind velocity was from local source, regardless of direction. To know the effect of long-range transport on pollution, a concentration weighted trajectory (CWT) model was analyzed based on a potential source contribution function (PSCF) model in which 75 percentiles high concentration was picked out for CWT analysis. $PM_{10}$, $PM_{2.5}$, OC, and EC were dominantly contributed from China in spring, and EC results were similar in both PSCF and CWT. In conclusion, Seoul air quality in spring was mainly affected by a mixture of local pollution and anthropogenic pollutants originated in China than the Asian dust.

• 한국토양비료학회지
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• 제37권3호
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• pp.143-148
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• 2004

국내 원예산업의 발달에 따라 다양한 종류의 배지 이용이 급속히 증가되고 있다. 현재 국내에서 사용중인 유기성 배지에는 피트모스, 코이어, 바크, 왕겨, 톱밥 등이 있으며, 무기성 배지로는 펄라이트, 버미큘라이트, 암면, 클레이볼 등이 있다. 본 연구는 유럽표준배지분석방법에 따라 원예용 배지를 분석하여 이들의 물리화학적 특성을 구명하고자 수행되었다. 국내에서 사용 중인 몇 가지 배지를 분석한 결과, 유기성 배지인 피트모스, 코이어, 바크, 톱밥, 왕겨는 종류, 원산지, 가공방법 등에 따라, 무기성 배지인 펄라이트, 버미플라이트, 입상암면, 클레이볼은 종류, 입자크기 등에 따라 이들의 물리화학적 특성의 차이를 보였다. 앞으로 유럽 표준분석방법 뿐만 아니라 국내 표준배지분석법에 따라 더 많은 배지재료와 혼합배지 및 상토를 분석함으로써 국내 배지분석법의 정립, 이상적인 배지의 기준 제시, 두 분석방법간의 환산인자확보 등의 연구가 요구된다.

• 환경위생공학
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• 제24권4호
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• pp.1-26
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• 2009

We conclude the following with air pollution data measured from city measurement net administered and managed in Gwangju for the last 7 years from January in 2001 to December in 2007. In addition, some major statistics governed by Gwangju city and data administered by Gwangju as national official statistics obtained by estimating the amount of national air pollutant emission from National Institute of Environmental Research were used. The results are as follows ; 1. The distribution by main managements of air emission factory is the following ; Gwangju City Hall(67.8%) > Gwangsan District Office(13.6%) > Buk District Office(9.8%) > Seo District Office(5.5%) > Nam District Office(3.0%) > Dong District Office(0.3%) and the distribution by districts of air emission factory ; Buk District(32.8%) > Gwangsan District(22.4%) > Seo District(21.8%) > Nam District(14.9%) > Dong District(8.1%). That by types(Year 2004~2007 average) is also following ; Type 5(45.2%) > Type 4(40.7%) > Type 3(8.6%) > Type 2(3.2%) > Type 1(2.2%) and the most of them are small size of factory, Type 4 and 5. 2. The distribution by districts of the number of car registrations is the following ; Buk District(32.8%) > Gwangsan District(22.4%) > Seo District(21.8%) > Nam District(14.9%) > Dong District(8.1%) and the distribution by use of car fuel in 2001 ; Gasoline(56.3%) > Diesel(30.3%) > LPG(13.4%) > etc.(0.2%). In 2007, there was no ranking change ; Gasoline(47.8%) > Diesel(35.6%) > LPG(16.2%) >etc.(0.4%). The number of gasoline cars increased slightly, but that of diesel and LPG cars increased remarkably. 3. The distribution by items of the amount of air pollutant emission in Gwangju is the following; CO(36.7%) > NOx(32.7%) > VOC(26.7%) > SOx(2.3%) > PM-10(1.5%). The amount of CO and NOx, which are generally generated from cars, is very large percentage among them. 4. The distribution by mean of air pollutant emission(SOx, NOx, CO, VOC, PM-10) of each county for 5 years(2001~2005) is the following ; Buk District(31.0%) > Gwangsan District(28.2%) > Seo District(20.4%) > Nam District(12.5%) > Dong District(7.9%). The amount of air pollutant emission in Buk District, which has the most population, car registrations, and air pollutant emission businesses, was the highest. On the other hand, that of air pollutant emission in Dong District, which has the least population, car registrations, and air pollutant emission businesses, was the least. 5. The average rates of SOx for 5 years(2001~2005) in Gwangju is the following ; Non industrial combustion(59.5%) > Combustion in manufacturing industry(20.4%) > Road transportation(11.4%) > Non-road transportation(3.8%) > Waste disposal(3.7%) > Production process(1.1%). And the distribution of average amount of SOx emission of each county is shown as Gwangsan District(33.3%) > Buk District(28.0%) > Seo District(19.3%) > Nam District(10.2%) > Dong District(9.1%). 6. The distribution of the amount of NOx emission in Gwangju is shown as Road transportation(59.1%) > Non-road transportation(18.9%) > Non industrial combustion(13.3%) > Combustion in manufacturing industry(6.9%) > Waste disposal(1.6%) > Production process(0.1%). And the distribution of the amount of NOx emission from each county is the following ; Buk District(30.7%) > Gwangsan District(28.8%) > Seo District(20.5%) > Nam District(12.2%) > Dong District(7.8%). 7. The distribution of the amount of carbon monoxide emission in Gwangju is shown as Road transportation(82.0%) > Non industrial combustion(10.6%) > Non-road transportation(5.4%) > Combustion in manufacturing industry(1.7%) > Waste disposal(0.3%). And the distribution of the amount of carbon monoxide emission from each county is the following ; Buk District(33.0%) > Seo District(22.3%) > Gwangsan District(21.3%) > Nam District(14.3%) > Dong District(9.1%). 8. The distribution of the amount of Volatile Organic Compound emission in Gwangju is shown as Solvent utilization(69.5%) > Road transportation(19.8%) > Energy storage & transport(4.4%) > Non-road transportation(2.8%) > Waste disposal(2.4%) > Non industrial combustion(0.5%) > Production process(0.4%) > Combustion in manufacturing industry(0.3%). And the distribution of the amount of Volatile Organic Compound emission from each county is the following ; Gwangsan District(36.8%) > Buk District(28.7%) > Seo District(17.8%) > Nam District(10.4%) > Dong District(6.3%). 9. The distribution of the amount of minute dust emission in Gwangju is shown as Road transportation(76.7%) > Non-road transportation(16.3%) > Non industrial combustion(6.1%) > Combustion in manufacturing industry(0.7%) > Waste disposal(0.2%) > Production process(0.1%). And the distribution of the amount of minute dust emission from each county is the following ; Buk District(32.8%) > Gwangsan District(26.0%) > Seo District(19.5%) > Nam District(13.2%) > Dong District(8.5%). 10. According to the major source of emission of each items, that of oxides of sulfur is Non industrial combustion, heating of residence, business and agriculture and stockbreeding. And that of NOx, carbon monoxide, minute dust is Road transportation, emission of cars and two-wheeled vehicles. Also, that of VOC is Solvent utilization emission facilities due to Solvent utilization. 11. The concentration of sulfurous acid gas has been 0.004ppm since 2001 and there has not been no concentration change year by year. It is considered that the use of sulfurous acid gas is now reaching to the stabilization stage. This is found by the facts that the use of fuel is steadily changing from solid or liquid fuel to low sulfur liquid fuel containing very little amount of sulfur element or gas, so that nearly no change in concentration has been shown regularly. 12. Concerning changes of the concentration of throughout time, the concentration of NO has been shown relatively higher than that of $NO_2$ between 6AM~1PM and the concentration of $NO_2$ higher during the other time. The concentration of NOx(NO, $NO_2$) has been relatively high during weekday evenings. This result shows that there is correlation between the concentration of NOx and car traffics as we can see the Road transportation which accounts for 59.1% among the amount of NOx emission. 13. 49.1~61.2% of PM-10 shows PM-2.5 concerning the relationship between PM-10 and PM-2.5 and PM-2.5 among dust accounts for 45.4%~44.5% of PM-10 during March and April which is the lowest rates. This proves that particles of yellow sand that are bigger than the size $2.5\;{\mu}m$ are sent more than those that are smaller from China. This result shows that particles smaller than $2.5\;{\mu}m$ among dust exist much during July~August and December~January and 76.7% of minute dust is proved to be road transportation in Gwangju.

• 한국토양비료학회지
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• 제37권1호
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• pp.1-6
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• 2004

각종 농업생산 활동을 통해 배출되는 유기성 부산물을 자원으로 재활용하기 위하여 퇴비화시켜 사용하고 있다. 퇴비화에 의한 재활용은 식물양분의 공급뿐 아니라 토양의 물리, 화학, 생물학적 특성의 개량을 가져올 수 있다. 그러나 국내에서 시판되는 퇴비의 경우 부재료 관리 등에 한계성이 있어, 중금속 등의 유해물질을 함유하거나 미부숙된 비료가 유통되고 있는 실정이다. 본 연구에서는 시판되고 있는 부산물비료의 화학적 특성을 파악하기 위하여 전국 각지에서 생산되는 약 600여종의 시판품 중에서 100 여종을 입수하여 화학성 및 유해물질 함량을 분석하였다. 실험결과 부산물 비료의 중금속 (Cd. Pb, Cu, Cr) 함량과 OM/N의 경우 좌측으로 극편향된 분포를 보여서 집단의 대표 값으로는 평균 보다는 중위값이 적합하다고 판단되었다. 한편 현재의 품질기준을 넘어서는 부산물비료의 출현빈도는 낮았지만, 그 비료들 중의 유해물질 함량은 전체 분석시료의 중위값보다 훨씬 큰 값을 보였다. 이상과 같은 결과로부터 부산물비료 각각의 품질 평가에는 중위값, 우리나라에서 생산되는 부산물비료 전체가 미치는 영향의 파악에는 가중평균값을 이용하는 것이 합리적이라고 판단할 수 있었다.

• 한국대기환경학회지
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• 제19권5호
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• pp.469-490
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• 2003

Atmospheric concentrations of persistent organic pollutants (POPs) were measured at Gosan, Jeju in November 2001 and spring 2002, each time for two weeks. Primary target pollutants were organochlorine pesticides, coplanar polychlorinated biphenyls (co- PCBs), and dioxin/furans listed in the Stockholm Convention adopted in May 2001. Polycyclic aromatic hydrocarbons (PAHs) were also measured in order to understand the overall characteristics of the POPs distribution as well as PM$_{2.5}$, a potent carrier of POPs. In the latter part of the measurement period of November 2001, almost every pollutant of combustion origin including dioxin/furans went high probably due to influence of emissions in the nearby area. The characteristics of atmospheric environment at Gosan in this period were rather close to urban areas far from those of a background area. A severe dust storm swept for three days at the end of the measurement period of spring 2002. However, changes in pollutant concentrations were relatively small except PM$_{10}$. Nevertheless, increases in particulate PAHs and OCDD (octachlorinated dibenzo-p-dioxins), mostly present in fine particles, were observed. Trends in organochlorine pesticide variations were mixed although possible volatilization of DDT residues from soil was inferred from the measurements of spring 2002.2.2.

• 한국표면공학회지
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• 제54권4호
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• pp.209-214
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• 2021

As coffee consumption per person increases annually to 323 cups in 2018, treating the spent coffee ground has arisen because spent coffee ground results in soil and air pollution. The demands of air purification filters are increasing more and more because the air pollution due to the fine dust has become worse. The spent coffee grounds had a porous structure, however, the pore was blocked by organic oil compounds. Electrocoagulation, which is one of the electrochemical methods, has the potential to remove the organic compounds. The surface area of spent coffee grounds increased effectively after the electrocoagulation treatment, and surface morphology and surface area were confirmed using SEM and BET, respectively. Using the FT-IR, both the spent coffee grounds and the electrocoagulated spent coffee grounds were characterized. The filter characteristics were examined by the adsorption test using formaldehyde, one of the air pollutants.

• 한국대기환경학회지
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• 제29권3호
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• pp.237-250
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• 2013

At Gosan ABC superstation in Jeju Island, we measured organic carbon (OC) and elemental carbon (EC) in $PM_{2.5}$ from October 2009 to June 2010 using a Sunset Laboratory Model-4 Semi-Continuous OC/EC Field Analyzer. It employs TOT (Thermal-Optical-Transmittance) method with NIOSH 5040 protocol and enables to continuously monitor OC and EC concentrations with 1-hour time resolution. The mean values of OC and EC for the entire period of measurements were $2.1{\pm}1.4{\mu}g/m^3$ and $0.7{\pm}0.6{\mu}g/m^3$, respectively. The OC/EC ratio was 3 and EC accounted $25{\pm}2.1%$ of total carbon (TC, TC=OC+EC). Although OC and EC showed similar trend in seasonal variation, the ratio of OC to EC was the highest in early summer when temperature was the highest and the air was affected by biomass burning in the southern part of China. In winter, the high OC and EC concentrations were likely influenced by increased coal combustion from residential heating. The high OC and EC concentrations were observed during events such as haze, dust, and the combination of the two. During the haze events, OC and EC were enhanced with increase in $PM_{10}$, $PM_{2.5}$, $SO_2$, and $NO_2$ with broad maxima. When dust occurred, both OC and EC started decreasing after reaching their maxima a couple of hours before $PM_{10}$ maximum. The peak separation of carbonaceous species and aerosol masses with time was more noticeable when haze event was followed by dust plume. These results confirm that OC and EC are key components of haze occurring in the study region.

• 분석과학
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• 제27권5호
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• pp.254-260
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• 2014

본 연구에서는 열처리 공정에서 발생하는 폐기물 중 무기물질류 15 종과, 유기물질류 24 종 (PCDD/PCDFs, PAHs)에 대한 배출 특성을 파악하고자 수행하였다. 납 열적 야금에서 발생하는 폐기물 (EWC 10 04)에서 규제 무기금속물질류 중 Pb은 가장 높은 농도를 보였다. 이는 EWC 10 04에서 분진으로 인한 결과로 판단된다. 아연 열적 야금에서 발생하는 폐기물(EWC 10 05)에서 규제 무기금속물질류 중 Zn이 높은 농도로 나타나 EWC 10 05에서 분진으로 인한 결과로 판단되며, 또한 구리 열적 야금에서 발생하는 폐기물(EWC 10 06)에서 Cu가 65,177 mg/kg으로 규제기준 (100 mg/kg)보다 651 배 높게 나타난 것은 EWC 10 06에서 분진으로 인한 결과로 판단된다. 분진은 다이옥신 0.0005~11.748 ng-TEQ/g으로 검출되었고, 소각재는 0.0027 ng-TEQ/g로 나타났다. 다이옥신의 규제기준을 초과하는 시료는 없는 것으로 조사되었다. PAHs의 함량은 Naphthalene는 ND~118.9 mg/kg, Phenanthrene는 ND~9.6 mg/kg, Benzo[b]fluoranthene은 ND~48.4 mg/kg, Benzo[a]pyrene는 ND~62.6 mg/kg, Fluoranthene는 ND~10.7 mg/kg, Benzo[a]anthracene는 ND~11.5 mg/kg의 범위로 나타났다.