• 기술사
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• 제34권1호
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• pp.59-65
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• 2001

Imported China Jades are mostly talc and serpentine groups, and that's occured troubles for our health and life of living organism. Serpentine is a group of common rock-forming minerals having the formula:(Mg$.$Fe)$^3$Si$_2$O$\_$5/(OH)$_4$. Sometime, simulated by nephrite or jade and translucent varieties we used for ornamental and decorative purposes. But it's forbid by heating materials for sauna and heating mats etc. that reason are it's occured asbestos dusts(chrysotile dusts) easily by the beating operations.

• 기술사
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• 제34권1호
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• pp.66-73
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• 2001

Imported China Jades are mostly talc and serpentine groups, and that's occured troubles for our health and life of living organism. Serpentine is a group of common rock-forming minerals having the formula : (Mg$.$Fe)$_3$Si$_2$O$\_$5/(OH)$_4$. Sometime, simulated by nephrite or jade and translucent varieties are used for ornamental and decorative purposes. But it's forbid by beating materials for sauna and heating mats etc. that reason are it's occured asbestos dusts (chrysotile dusts) easily by the heating operations.

• 한국산업보건학회지
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• 제20권4호
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• pp.263-273
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• 2010

Occupational exposure to wollastonite can occur during its mining, processing and using. Wollastonite was analyzed for its physicochemical properties by transmission electron microscope and scanning electron microscope equipped with energy dispersive X-ray spectrometer. Wollastonite fibers were 3.3${\mu}m$ in diameter(av.) and were 30.5${\mu}m$ in length(av.). The atomic composition of wollastonite was Si 56.41% and Ca 43.59%. Respiratory toxicity of wollastonite has been studied in term sequential in Sprague-Dawely rats. UICC chrysotile (average diameter 0.03${\mu}m$, average length 2.93${\mu}m$) was applied as the positive control. The effects of 2mg wollastonite on respiratory system and pathological changes were evaluated after 1, 4, 8, 12 weeks instilled into rat lungs. Inflammation response broke out from 1 week after instilled with wollastonite and the pathological examination further showed increased legions of granulomatous inflammation after 4 weeks, but decreased granulomatous inflammation after 8 weeks, whereas chrysotile induced progressive interstitial granulomatous inflammation and fibrosis as a function of time.

• 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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• 제6권2호
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• pp.165-175
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• 1996

Fourteen(14) large commercial buildings located in Seoul with friable sprayed-on surface insulation material on ceiling were investigated for fiber types in bulk material and for airborne fiber concentrations in buildings by transmission electron microscopy (TEM) in order to compare the results with those by polarized light microscopy (PLM) and phase contrast microscopy (PCM). The results were as follows: 1. Chrysotile asbestos was found in one bulk sample out of total 14 bulk samples collected. Glass fiber and mineral wool were the two major constituents of the bulk samples. 2. The Na-Mg-Si-Ca-Fe-Al ratios of the EDX spectra which were normalized with the Si peak were 0-1.0-10-8.3-4.0-4.0 in mineral wool and 0-5-10-21-0-0 in chrysotile asbestos, respectively. 3. Airborne fiber concentrations were log-normalcy distributed and the geometric mean (geometric standard deviation) fiber concentrations by TEM in the underground parking lots and inside buildings were 0.0048 f/cc(1.93) and 0.0040 f/cc(2.27), respectively with no statistical difference. In the outdoor ambient air, statistically significantly lower concentration of 0.0018 f/cc(2.04) was measured. 4. The TEM/PCM ratios of airborne fiber concentrations ranged 0.5 - 2.0 for 80 % of airborne samples analyzed, end the regression equation between TEM and PCM was PCM=-0.2724+1.1355(TEM) with the coefficient of determination $R^2=0.52$. The results of this study confirmed that the sprayed-on surface insulation material found in some commercial buildings may possibly be contaminated with asbestos fiber. Since statistically significant relationship of fiber concentrations measured by PCM and TEM inside buildings and ambient air was found, previous results by PCM in ambient air could be used to estimate the ambient fiber concentrations in knowing the ratio of TEM/PCM.

• 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.

• 환경위생공학
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• 제18권1호
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• pp.8-14
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• 2003

Asbestos is composed of long thin fibers approximately diameter $0.02\mu\textrm{m}$ and flexibility, strength, electrical, thermal conditions. The most common asbestos are : Chrysotile(white), Crocidolite(Blue), Amosite(Brown). Asbestos was first introduced in the Korea in 1960 and installation of these products continue through the late 1970's and even the early 1980's. Bu-pyung basement stores in Korea were surveyed from September 25 to October 26, 2001. The purpose of this research was to evaluate worker-exposure to asbestos, comparing to the standards and to research notice of inhabitants about asbestos. Fifteen personal samples and six areas were collected using Gillian Air Sampler. Result of this research were as follows. 1. The most of asbestos exposure concentrations keeps to the criterion(OSHA(Occupational Safety and Health Adminisoation), NIOSH) but forty three percent of the Six samples exceeded the EPA (Environmental protection Agency) of 0.01 fibers/cc. 2. All of places compliced to the standards but there is no "Safe level" of asbestos exposure to the people. Especially people who are expose more frequently over a long time are more at risk.

• 자원환경지질
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• 제26권1호
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• pp.1-10
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• 1993

The Andong serpentinite body is distributed along the Andong fault, and shows an elliptical shape. The serpentinite is composed of serpentine minerals and other various minerals such as forsterite, pyroxene, talc, tremolite, chlorite, prehnite, calcite and dolomite. The serpentine minerals consist primarily of lizardite with minor chrysotile. Antigorite rarely occurs in some veins. The serpentinite is largely divided into two alteration zones by the occurrence and mineral assemblages. One of the alteration zones is composed of a large amount of serpentine minerals. The other is characterized by tremolite and chlorite. The alteration zone composed of tremolite and chlorite seems to have been formed by hydrothermal alteration after the formation of serpentinite. It is considered that the serpentinite have been formed by alteration of the ultramafic rock such as peridotite.

• 한국산업보건학회지
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• 제19권1호
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• pp.8-15
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• 2009

This study was examined to find out asbestos exposure level the factors which affected the level at asbestos abatement sites. We visited a total of thirteen building demolition sites(3 apartments, 3 schools, 4 stores, and 3 houses) were visited to collect samples and related data from August to November, 2006. The results of this study were as follows 1. The results of an analysis of bulk samples to identify types of asbestos at the asbestos abatement sites showed that the kinds of the asbestos detected were chrysotile by 50.0%, were tremolite by 2.6%, and were the contents of chrysotile by 3 to 20%. 2. The geometric mean concentration of asbestos was 0.007 f/cc(range 0.001-0.34 f/cc) and its geometric standard deviation was 5.83. Of the samples, however, 12 exceeded the Korean Occupational Exposure Limit(0.1f/cc). 3. Of the materials, textile material had the highest concentration with geometric mean of 0.016 f/cc. When asbestos-containing materials were removed using T type tools, the geometric mean concentration of asbestos was 0.061 f/cc. The level by this method was much higher than by other removal methods. In analysis by the type of building, the geometric mean concentration of asbestos in stores was 0.042 f/cc and was higher than in other buildings. 4. The Poisson regression analysis was applied to find out the factors that affect the airborne asbestos concentration. As a result of the analysis, removal using a T type tool was the most important factor affecting the asbestos concentration(p<0.01). In conclusion, the airborne asbestos concentration(geometric mean) in asbestos abatement sites was 0.007 f/cc(0.001~0.34 f/cc), and 12(14.6%) of all samples were over the 0.1 f/cc. These results showed that asbestos abatement workers have been exposed to the high level of airborne asbestos because they have not been keeping asbestos removal rule. In accordance with increases of the number of building demolition sites, the better government regulation on asbestos abatement methods should be made and be performed well at building demolition sites.

• 한국광물학회지
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• 제25권1호
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• pp.9-21
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• 2012

우리나라에는 약 6개소의 사문석광산이 존재하였으며, 그 중에 최근까지 채굴되었던 충남지역의 비봉광산에 대하여 구성광물의 산출상태, 특성 및 성인을 검토하였다. X-선회절분석, X-선형광분석, 주사현미분석, 전자현미분석, 적외선분광분석, 편광현미경관찰 등을 통하여 사문석의 광물학적 특성을 조사하였다. 비봉광산의 사문암체는 선캠브리아기의 변성퇴적암을 관입한 형태로 소규모로 분포하여 나타나며, 사문석, 포스터라이트, 휘석, 투각섬석, 자철석, 녹니석, 운모, 활석, 돌로마이트 등의 다양한 광물들이 산출되었다. 사문암체의 광물조합은 크게 A) 사문석-포스터라이트, B) 사문석, C) 사문석-녹니석(버미큘라이트), D) 사문석-투각섬석, E) 투각섬석-녹니석의 5가지로 구분되어 나타났다. 사문석광물은 리자르다이트와 안티고라이트가 주로 포함되며 크리소타일은 일부 부분적으로 포함되어 산출되는 것으로 나타났다. 사문암체의 구성광물과 그 산출상태로 보아 포스터라이트를 주성분으로 하는 초염기성암의 열수변질작용에 의해 사문석이 형성되었으며, 그후 2차적인 열수작용에 의해 녹니석과 투각섬석 등의 변질광물이 형성된 것으로 나타났다.