• 한국신재생에너지학회:학술대회논문집
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• 한국신재생에너지학회 2010년도 추계학술대회 초록집
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• pp.159.2-159.2
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• 2010

Asbestos is the collective name for a group of naturally occurring minerals in their fibrous form and hydrous silicates of magnesium and a mineral fiber that has been used commonly in a variety of building construction materials for insulation and as a fire-retardant. Asbestos has been used for a wide range of manufactured goods, because of its fiber strength and heat resistant properties. Nevertheless harmful of asbestos is quite serious. Exposure to airborne friable asbestos may result in a potential health risk because persons breathing the air may breathe in asbestos fibers. Continued exposure can increase the amount of fibers that remain in the lung. Fibers embedded in lung tissue over time may cause serious lung diseases including asbestosis, lung cancer. In this paper, we carried out as fundamental study for dispose of asbestos cement slate safely and perfectly. Melting Temperature of asbestos need to more than $1,520^{\circ}C$ and specially asbestos cement slate need more energy than that of pure asbestos. We need to decrease melting temperature of asbestos cement slate for economical efficiency. To the purpose, glass and bottom ash were chosen as additives for basicity control. we analyzed about properties of asbestos cements slate, melting characteristics on the additives ratio and temperature. We confirmed about harmlessness of melting slag through analysis of scanning electron microscope(SEM) and x-ray diffractometer(XRD).

• 한국환경과학회지
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• 제24권7호
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• pp.927-937
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• 2015

This study was performed to identify and quantify the asbestos fibers released from two types of asbestos-cement slate roofs. One is a plant roof installed in 1987 which contained 15% chrysotile, and the other is a residential roof installed before 1983 which contained 12% chrysotile. The concentrations of asbestos fibers in air surrounding asbestos-cement slate roofs and in the falling water harvested from the same roofs on rainy days ranged from 0.0012 to 0.0018 f/mL and from 1,764 f/L to 10,584 f/L, respectively. The concentration of inorganic fibers in the soil around asbestos-cement slate roofs was from 217 to 348 f/g. With the above results, the excess lifetime cancer risk (ELCR) for the risk assessment of the asbestos fibers released from asbestos-cement slate based on US EPA IRIS (Integrated risk information system) model is within 5.5E-06 ~ 6.5E-06 levels which indicates that the levels do not exceed "the acceptable risk(1.0E-05)" recommended by WHO. The asbestos concentration in air, drained rainfall and soil around the plant slate roof was higher than that around residential slate roof, but the excess lifetime cancer risk (ELCR) from residential slate was higher than that from plant slate. This suggested that the enclose and encapsulation of residential roofs have priority in removal policy to minimize the exposure risk.

• 한국산업보건학회지
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• 제23권3호
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• pp.196-204
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• 2013

Objectives: The purpose of this study is to analyze the number and influence factors of asbestos fibers in the air of farmhouses with asbestos cement slate roofing, as well as in rainwater per unit area of the asbestos cement slate roofing. Methods: At a distance of 1 m from the end of asbestos cement slate roofing in 20 farmhouses, the asbestos fiber in the air was collected three times on a clear day downwind from the prevailing wind. Rainwater falling from the slate roofing was collected four times with a 1.05-m rainwater pipe on a rainy day at the 20 farmhouses, filtered with a MCE filter, and analyzed with a phase contrast microscope. Results: The geometric mean of the number of asbestos fibers in the air of farmhouses with slate roofing was 0.11 fiber/L, and no samples exceeded the recommended standard of 10 fiber/L. As a result of multiple regression analysis, a factor which gave a significant influence to the asbestos fiber content in the air was the gross area of slate roofing at the target farmhouses. The number of asbestos fibers included in rainwater collected per 1 m2 of slate roofing was 1,753 fiber/$L{\cdot}m2$. As a result of multiple regression analysis, the number of asbestos fibers contained in rainwater per 1 m2 of slate showed a significantly higher tendency as the year of slate roofing installation at the target farmhouses receded. Conclusions: It was confirmed for the first time in Korea that asbestos from asbestos cement slate roofing scatters into the air.

• 한국안전학회지
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• 제29권6호
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• pp.137-143
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• 2014

Asbestos is given to a variety of six naturally occurring silicate minerals. These minerals possess high tensile strength, flexibility, resistance to chemical and thermal degradation, and electrical resistance. These minerals have been used for decades in thousands of commercial products, such as insulation and fireproofing materials, automotive brakes, textile products, cement and wallboard materials. When handled, asbestos can separate into microscopic-size particles that remain in the air and are easily inhaled. It is now known that prolonged inhalation of asbestos fibers can cause serious and fatal illnesses including malignant lung cancer, mesothelioma, and asbestosis. Therefore the use of asbestos and asbestos products has dramatically decreased in recent years. Also all constructions including asbestos should be removed under strictly controlled conditions and very tightly implemented health & safety management systems. In this study, the process of the removal work of the asbestos cement slate was analyzed by IDEF-0 modeling and evaluated by 4M risk assessment method. The results show that removal work of the asbestos cement slate was classified five process and eighteen detail process. The risk of safety side the higher than the risk of health side in 4M risk assessment.

• 자원환경지질
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• 제52권6호
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• pp.627-635
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• 2019

슬레이트는 석면을 이용한 대표적인 건축자재 중 하나로써 백석면(10~20%)과 시멘트 성분을 결합하여 만든 제품이다. 슬레이트에 포함되어 있는 석면은 인체에 유입되면 세포 손상이나 변형을 일으키고 체외로 잘 배출되지 않아 폐암, 석면폐, 악성중피종 및 흉막비후 등과 같은 질병을 일으키는 원인이 되는 것으로 입증되어 1977년 세계보건기구(WHO) 산하 국제암연구소(IARC)에서는 1군 발암물질로 지정하였다. 현재 이러한 슬레이트는 대부분 지정매립장에 매립하여 처리하고 있으나 매립용량이 한계에 다다르고 있고 매립한다고 하여도 추후 외부환경으로 노출될 수 있는 잠재적인 위험성이 있어 매립 처리방법 이외에 슬레이트에 포함된 석면을 무해화하여 안전하게 처리할 수 있는 방법이 필요하다. 따라서 이 연구에서는 발열반응 촉매제와 열처리를 이용하여 슬레이트에 함유된 석면 무해화 가능성을 확인하고자 하였다. 실험은 석면해체·제거 사업장에서 발생한 석면함유 슬레이트를 이용하였고 발열반응 촉매제는 염화칼슘(CaCl₂), 염화마그네슘(MgCl₂), 수산화나트륨(NaOH), 규산소듐(Na₂SiO₃), 카올린[Al₂Si₂O₅(OH)₄)], 활석[Mg₃Si₄O₁₀(OH)₂]을 이용하여 총 6가지의 촉매제를 제조하였다. 6가지의 촉매제를 슬레이트에 각각 도포한 후 열중량-시차열분석(TG-DTA)을 실시하여 분석결과를 토대로 슬레이트 무해화를 위한 열처리 온도를 750℃로 결정하였다. 슬레이트에 6가지 촉매제를 각각 도포한 후 750℃에서 2시간 열처리하여 X-선 회절 분석(XRD), 주사전자현미경 분석(SEM-EDS), 투과전자현미경 분석(TEM-EDS)을 한 결과 슬레이트 내 백석면[chrysotile, Mg₃Si₂O₅(OH₅)]이 주상의 고토감람석(forsterite, Mg₂SiO₄)으로 상전이 됨을 확인하였다. 또한, 슬레이트 원시료와 발열반응 촉매제 도포 후 열처리한 시료에 물리적인 힘을 가하여 광물의 형상 변화를 비교 관찰한 결과, 슬레이트 내 백석면은 섬유형을 유지하였으나 촉매제 도포 및 열처리를 한 시료는 무정형 형태로 깨지는 것을 확인할 수 있었다. 따라서 발열반응 촉매제와 열처리를 통하여 낮은 온도에서 경제적으로 석면함유 슬레이트를 안전하게 처리할 수 있는 하나의 방안을 제시할 수 있을 것으로 사료된다.

• 광물과 암석
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• 제33권4호
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• pp.407-417
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• 2020

국내 폐슬레이트 발생량은 매년 증가 추세로 지정매립장 용량이 한계에 다다르고 있어 슬레이트를 대용량으로 안전하고 저렴하게 처리함과 동시에 재활용할 수 있는 방법이 필요하다. 이에 대한 대안으로 시멘트 소성로를 이용한 폐슬레이트 열처리 방법을 들 수 있다. 이 연구에서는 플라즈마를 이용하여 시멘트 소성로의 고온 환경을 모사할 수 있는 중간 규모(pilot scale)의 장치를 개발하고 이를 이용하여 폐슬레이트 내석면의 비활성화 및 시멘트 원료로의 재활용 가능성을 확인하고자 하였다. 중간규모 실험 장치는 플라즈마 토치를 이용하여 실제 소성로와 동일한 조건을 가지도록 1/50로 축소·제작하였다. 실험조건은 시멘트 소성로의 소성 시간과 동일하게 20분간 200-2,000℃까지 100℃ 간격으로 온도를 상승시키며 폐슬레이트의 비활성화 실험을 실시하였다. 플라즈마 고온반응기를 이용하여 열처리한 폐슬레이트의 XRD, PLM, TEM-EDS 분석결과, 1,500℃ 이상의 온도에서 슬레이트 내 백석면이 고토감람석으로 광물 상전이가 일어나 비활성화되고 시멘트 구성 광물인 라나이트(Ca2SiO4)가 형성됨을 확인하였다. 이 연구 결과는 추후 시멘트 소성로를 이용하여 대용량의 슬레이트를 경제적이고 안전하게 처리함과 동시에 시멘트 원료로 재활용할 수 있는 방안에 대한 기초자료로 활용할 수 있을 것으로 사료된다.

• Architectural research
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• 제13권2호
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• pp.31-40
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• 2011

Asbestos have been used around the world by physical and chemical characteristics that are a reliable and cost-effective. But asbestos, once called the miracle of mineral, is now a quiet time bomb. Asbestos hazards have been studied and the government has pursued 'Comprehensive Measures for Asbestos Management' jointly with related departments. As a part of plan, Ministry of Environment is to introduce legislation 'Asbestos Safety Management Act' through Environment Announcement No. 2010-108. The same Act. 24 shows as follows. Minister of Environment or governor should do survey on the actual condition targeting rural buildings with slates and partly or fully fund to dissolve, remove asbestos slate which was used in each building. However, the local survey was only conducted by each municipality regionally. And there is no actual condition data by area, application and year, and there was no data on disposal costs concerning asbestos slate buildings In this study, discharge of asbestos slate was calculated per unit area and formula was developed with regression analysis. In addition, Demolition, dismantling, disposal costs were computed via a phone survey to disposal companies and then this study proposed standards for this.

• 한국산업보건학회지
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• 제20권2호
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• pp.88-93
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• 2010

To confirm and quantify asbestos fibers released from the asbestos-cement slate roofs due to weathering, three houses, selected based on the year of built - 60's, 70, and 80's, were investigated. All of them were located in the downtown of Seoul. Rain or snow-melt water was collected from the roof in a 3.5 liter plastic bottle. A known amount of collected water was filtered on the 37 mm membrane filter, ashed in a muffle furnace, and subsequently treated with HCl to remove organic material. The treated remaining was refiltered on a 25mm membrane filter for PLM and PCM analyses. The NIOSH 7400 method was utilized for PCM counting. In addition, SEM/EDX was used to confirm the asbestos types. The results of this study showed that chrysotile fibers were confirmed by PLM in all samples analyzed. A significant amount of asbestos fibers were found in the water samples. The ranges of asbestos fibers counted from the samples collected in the 60's, 70's, and 80's were; 10,406.3~55,575.6 f/L, 5,218.8~38,126.2 f/L, and 2,906.3~7,798.6 f/L, respectively. As anticipated, concentrations of asbestos fibers increased with time of installment of the roofing material. We conclude that weathering can be a significant factor on the release of asbestos fibers from the asbestos cement products. Since asbestos fibers released into environment can be a source of significant health hazard, countermeasures, such as replacement, removal, and encapsulation of weathered asbestos slate, should be initiated immediately.

• KIEAE Journal
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• 제11권3호
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• pp.57-62
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• 2011

Asbestos have been used around the world because of reliable and cost-effective physicochemical characteristics. After incubation period about 15-40 years asbestos can cause various cancers, including malignant mesothelioma when inhaled into the air. These properties turned out, asbestos have been banned from using in developed countries. Also in Korea also, the use of asbestos was banned across the board by revision of Industry Safety and Health Act in February 2009. Therefore, the problem of asbestos is not when using. It is about dismantling, maintenance, and the final processing of asbestos waste. Asbestos Cement slates which is Widely distributed throughout the country as roofing materials has much scattering potential compare with inside materials. Also Ministry of Environment is planning to introduce legislation 'Asbestos Safety Management Act' through Environment Announcement and The same Act. 24 show as follows. Minister of Environment or governor should do survey on the actual condition targeting rural buildings with slates and partly or fully fund to dissolve, remove asbestos slate which was used in each buildings. Therefore, to solve these problems, database-building and necessity of management strategies have been continually arisen. So this study was performed. Its application value is very high in terms of its political, economic. Asbestos Cement Slates database could build to collect national registered building data and then using GIS, asbestos cement Slates distribution map were constructed in each province's cities and counties of the country. And this map by Application, construction was to visualize by application, construction of year. Through these results, information of Asbestos Cement Slates could visually inform to policy makers, asbestos dismantling and management contractor, and civilian and it would alleviate the gap of knowledge information. This is expected to be utilized by medium and long-term and effective plan for demolition and dismantling of asbestos cement Slates.

• 한국환경과학회지
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• 제22권12호
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• pp.1579-1587
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• 2013

This study was performed to evaluate the asbestos exposure levels and to calculate excess lifetime cancer risk (ELCR) for the risk assessment of the asbestos fibers released from asbestos-cement slate roofing (ASR) building. Total number of ASR buildings was into 21,267 in Busan, and 82.03 percent of the buildings was residential houses, and 43.61 percent of the buildings was constructed in 1970s. For this study, ten buildings were selected randomly among the ASR buildings. The range of airborne asbestos concentration in the selected ten ASR buildings was from 0.0016 to 0.0067 f/mL, and the concentration around no-admitted ASR buildings was higher than that around admitted buildings. The ELCR based on US EPA IRIS (integrated risk information system) model is within 3.5E-05 ~ 1.5E-04 levels, and the ELCR of no-admitted ASR buildings was higher than 1.0E-04 (one person per million) level that is considered a more aggressive approach to mitigate risk. These results indicate that the cancer risk from ASR buildings is higher than other buildings, and systematic public management is required for control of no-admitted ASR buildings within near future.