• 제목/요약/키워드: Geometric mean

검색결과 751건 처리시간 0.027초

Poisson 수요과정을 갖는 두 품목 콘윕시스템의 성능평가 (Performance Evaluation of a Two-Product CONWIP System with Poisson Demand Processes)

  • 박찬우;김수민;방우형;이효성
    • 대한산업공학회지
    • /
    • 제39권3호
    • /
    • pp.172-182
    • /
    • 2013
  • In this study we consider a flow line CONWIP system in which two types of product are produced. The processing times of each product type at each station follow an independent exponential distribution and the demands for the finished products of each type arrive according to a Poisson process. The demands that are not satisfied instantaneously are either backordered or lost according to the number of unsatisfied demands that exist at their arrival instants. For this system we develop an approximation method to obtain the performance measures such as steady state probabilities of the number of parts of each product type at each station, mean waiting times of backordered demands and the proportion of backordered demands. For the analysis of the proposed CONWIP system, we model the CONWIP system as a two class closed queueing network with a synchronization station and analyze the closed queueing network using a product-form approximation method for multiple classes developed by Baynat and Dallery. In the approximation method, each subsystem is analyzed using a matrix geometric method. Comparisons with simulation show that the approximation method provides fairly good results for all performance measures.

작업장에서의 n-부틸 글리시딜 에테르에 대한 건강 위험성 평가 (Human Health Risk Assessment of n-Butyl Glycidyl Ether from Occupational Workplaces)

  • 문형일;최현일;신새미;변상훈
    • 한국산업보건학회지
    • /
    • 제23권1호
    • /
    • pp.20-26
    • /
    • 2013
  • Objectives: This study was conducted to evaluate the health risk of workers exposed to butyl glycidyl ether to prevent them from developing occupational diseases. Methods: The workplaces that coat floor with epoxy were selected and the samples were collected and analyzed with NIOSH 1616 Method. We calculate workplace reference concentration using with NOAEL estimated by the study of Anderson et al. in 1978. Risk was calculated by the ratio of exposure to workplace reference concentration. Monte-Carlo simulation was performed to derivate the median, cumulative 90%, and cumulative 95% value by using Crystal Ball. Results: Butyl glycidyl ether is a skin, eye irritator and can result in central nervous system depression, allergic reaction. NOAEL was 38 ppm and workplace reference concentration was calculated as 0.73 ppm corrected with uncertainty factors. Geometric mean was 1.152 ppm and geometric standard deviation was 1.522 by the workplace environment measurement. The median, cumulative 90%, and cumulative 95% value of risk were calculated as 1.617, 1.934, and 2.092, respectively. Conclusions: Not only cumulative 90% and cumulative 95% value but also the median of risk is higher than 1.0 by the risk characterization, so it can do a lot of harm to workers. Therefore, the process of derivating workplace reference concentration and the appropriacy of the uncertainty factors should be re-examined.

금속제품 제조 산업장내 공기중 금속농도에 관한 연구 (A Study on Metal Concentrations in the Air of Metal Products Manufacturing Industry)

  • 강용선;김세동;구태형;윤형렬;문덕환;한용수
    • 한국산업보건학회지
    • /
    • 제6권2호
    • /
    • pp.249-264
    • /
    • 1996
  • This study was conducted for the purpose of obtaining the fundamental data on improvement of working environment and contributing to health improvement of workers who dealed with metal by assessing the metal concentration in air of industries located in Chang-Won Industrial Complex. Authors measured the concentration of metals(Al, Cd, Cr, Cu, Mn, Ni, Pb, Sn and Zn) is the air to 25 working processes of 73 industries by flame atomic absorption spectrometry from February to December 1994. Personal air sampler was used for air sampling with mixed cellulose-ester membrane filter. The results were as follows : 1. The geometric means(range) of metal concentration; 1) Al: $0.1505mg/m^3$ ($0.0147-18.6100mg/m^3$) 2) Cd: $0.0077mg/m^3$ ($0.0003-7.0710mg/m^3$) 3) Cr: $0.0163mg/m^3$ ($0.0013-1.1510mg/m^3$) 4) Cu: $0.0097mg/m^3$ ($0.0009-0.4950mg/m^3$) 5) Mn: $0.0412mg/m^3$ ($0.0006-4.7877mg/m^3$) 6) Ni: $0.0088mg/m^3$ ($0.0001-1.0170mg/m^3$) 7) Pb: $0.0152mg/m^3$ ($0.0015-0.4499mg/m^3$) 8) Sn: $0.0486mg/m^3$ ($0.0037-0.1500mg/m^3$) 9) Zn: $0.1911mg/m^3$ ($0.0122-8.2920mg/m^3$) 2. The geometric mean of lead exceeded TWA in assembling process of other general purpose machinery not elsewhere classified products manufacturing industries.

  • PDF

전자현미경을 이용한 건물내 비고형 표면자재의 석면 오염 및 기중 석면농도 특성조사 (Characterization of Asbestos Content in Friable Sprayed-on Surface Material and Airborne Asbestos Concentrations in Buildings by TEM)

  • 유성환;김현욱
    • 한국산업보건학회지
    • /
    • 제6권2호
    • /
    • pp.165-175
    • /
    • 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.

  • PDF

인공위성 레이더(SAR) 영상자료에 있어서 지형효과 저감을 위한 방사보정 (Topographic Normalization of Satellite Synthetic Aperture Radar(SAR) Imagery)

  • 이규성
    • 대한원격탐사학회지
    • /
    • 제13권1호
    • /
    • pp.57-73
    • /
    • 1997
  • 본 연구는 산악 지형의 레이더(SAR) 영상자료에서 흔히 볼 수 있는 지형의 기복에 의한 화소값의 왜곡 보정과 관련된 것이다. 연구 자료로는 RADARSAT 위성에서 얻어진 서울 남쪽 관악산과 안양 지역의 SAR 영상자료를 이용하였고, 영상자료의 보정을 위하여 SAR 영상과 유사 한 해상력을 갖춘 수치고도자료(digital elevation model)를 제작하였다. 레이더 영상자료는 먼저 각 화소가 가지고 있는 기하학적 왜곡을 보정하여 정확한 지도좌표에 등록함으로써, 수치고도자 료로부터 각 화소 지점의 구체적인 지형적 특성에 관한 자료를 산출하였다. 영상의 각 화소값에 미치는 지형적 영향을 분석하기 위한 기하학적 인자로서 각 지점에 입사되는 레이더파와 경사면 의 연직선이 이루는 유효입사각(local incidence angle)을 산출하였다. 수치지도로 제작된 임상도 를 이용하여 동일한 임분특성을 가지고 있는 산림내에서 얻어지는 레이더 반사치와 유효입사각의 관계를 분석하였다. 영상자료의 지형효과 보장은 실험적인 방법에 의하여 수행되었는데, 유효입사 각과 레이더 반사치와의 관계에서 도출된 지형에 의한 영향을 나타내는 수식을 적용하였다. 보정 결과는 육안에 의한 영상의 비교와 함께 현지자료를 이용하여 검증하였다.

카드뮴의 흡입독성 연구를 위해 설계된 에어로졸 발생장치에서 발생된 카드뮴 에어로졸의 입경분석(766ppm 카드뮴 네뷸라이징 용액) (Particle Size Analysis of Cadmium Aerosol for Cadmium Inhalation Toxicology Study (766ppm Cadmium Nebulizing Solution))

  • 정재열;도날드밀턴;김태형;이종영;장두섭;강성호;송용선;이기남
    • 동의생리병리학회지
    • /
    • 제16권5호
    • /
    • pp.1035-1041
    • /
    • 2002
  • Ultrasonic nebulizer with the application of new engineering methodology and the design of electronic circuit and 766ppm Cd nebulizing solution were used to generate cadmium aerosol for inhalation toxicology study. The results of particle size analysis for cadmium aerosol were as following. The highest particle counting for source temperature 20℃ was 43.449 x 10³ in inlet temperature 250℃ and particle diameter 0.75㎛. The highest particle counting for source temperature 50℃ was 43.211 x 10³ in inlet temperature 100 ℃ and particle diameter 0.75㎛. The highest particle counting for source temperature 70℃ was 41.917x10³ in inlet temperature 250℃ and particle diameter 0.75㎛. The ranges of geometric mean diameter(GMD) were 0.677-1.009㎛ in source temperature 20℃, 0.716-0.963㎛ in source temperature 50℃, and 0.724-0.957㎛ in source temperature 70℃. The smallest GMD was 0.677㎛ in source temperature 20℃ and inlet temperature 20℃. and the largest GMD was 1.009㎛ in source temperature 20℃ and inlet temperature 20℃. The ranges of geometric standard deviation(GSD) were 1.635-2.101 in source temperature 20℃. 1.676-2.073 in source temperature 50℃, and 1.687-2.051 in source temperature 70℃. The lowest GSD was 1.635 in source temperature 20℃ and inlet temperature 20℃, and the highest GSD was 2.101 in source temperature 20℃ and inlet temperature 200℃. Aerosol generated for cadmium inhalation toxicology study was polydisperse aerosol. The ranges of mass median diameter(MMD) were 1.399-5.270㎛ in source temperature 20℃. 1.593-4.742㎛ in source temperature 50℃, and 1.644-4.504㎛ in source temperature 70℃. The smallest MMD was 1.399㎛ in source temperature 20℃ and inlet temperature 20℃, and the largest MMD was 5.270㎛ in source temperature 20℃ and inlet temperature 200℃. Increasing trends for GMD, GSD, and MMD were observed with same source temperature and increase of inlet temperature. MMD for inhalation toxicology testing in EPA guidance is less than 4㎛. In our results. inlet temperature 20 and 50℃ in source temperature 20℃, and inlet temperature 20 to 150℃ in source temperature 50 and 70℃ were conformed to the EPA guidance. MMD for inhalation toxicology testing in OECD and EU is less than 3㎛. In our results, inlet temperature 20 and 50℃ in source temperature 20, 50, and 70℃ were conformed to the OECD and EU guidance.

흡입독성 연구를 위한 2730ppm 납 네뷸라이징 용액에서 발생된 에어로졸의 입경분석 (Particle Size Analysis of Lead Aerosol with the use of 2730ppm Lead Nebulizing Solution for Inhalation Toxicology Study)

  • 정재열;강성호;김삼태;이은경;송용선;이기남
    • 동의생리병리학회지
    • /
    • 제17권2호
    • /
    • pp.518-524
    • /
    • 2003
  • Ultrasonic nebulizer with the application of new engineering methodology and the design of electronic circuit was made for lead inhalation toxicology study and 2730ppm lead nebulizing solution was used to generate lead aerosol. After modification of source and inlet temperatures, the results of particle size analysis for lead aerosol were as following. The highest particle counting for source temperature 20℃ was 39933.66 in inlet temperature 100℃ and particle diameter 0.75tLm. The highest particle counting for source temperature 50℃ was 39992.71 in inlet temperature 250℃ and particle diameter 0.75μm. The highest particle counting for source temperature 70℃ was 37569.55 in inlet temperature 50℃ and particle diameter 0.75μm. The ranges of geometric mean diameter(GMD) were 0.754-0.784μm for source temperature 2℃, 0.758-0.852μm for source temperature 50℃, and 0.869-1.060μm for source temperature 70℃. The smallest GMD was 0.754μm in source temperature 20℃ and inlet temperature 20℃, and the largest GMD was 1.060μm in source temperature 70℃ and inlet temperature 250℃. The ranges of geometric standard deviation(GSD) were 1.730-1.782 for source temperature 20℃, 1.734-1.894 for source temperature 50℃, and 1.921-2.148 for source temperature 70℃. The lowest GSD was 1.730 in source temperature 20℃ and inlet temperature 20℃, and the highest GSD was 2.148 in source temperature 70℃ and inlet temperature 250℃. Lead aerosol generated in this study was polydisperse. The ranges of mass median diameter(MMD) were 1.856-2.133μm for source temperature 20℃, 1.877-2.894μm for source temperature 50℃, and 3.120-6.109μm for source temperature 70℃. The smallest MMD was 1.856μm in source temperature 20℃ and inlet temperature 20℃, and the largest MMD was 6.109μm in source temperature 70℃ and inlet temperature 250℃. Slight increases for GMD, GSD, and MMD values were observed with same source temperature and increase of inlet temperature. MMD for inhalation toxicology testing in EPA guidance is less than 4μm. In this study, source temperature 20℃ and 50℃ with inlet temperature from 20℃ to 250℃ were conformed to the EPA guidance, but inlet temperature 20℃ and 50℃ for source temperature 70℃ were conformed EPA guidance. MMD for inhalation toxicology testing in OECD and EU is less than 3μm. In this study, source temperature 20℃ and 50℃ with inlet temperature from 20℃ to 250℃ were conformed to the EPA guidance, but none for source temperature 70℃.

일부 합성피혁 근로자들의 Dimethylformamide, Methyl Ethyl Ketone, Toluene 노출에 따른 요중 대사물질 (Urinary Metabolites of Dimethylformamide, Methyl Ethyl Ketone, and Toluene exposed Workers in Synthetic Leather Factories)

  • 최호춘;김강윤;안선희;이영자;정규철
    • 한국산업보건학회지
    • /
    • 제11권2호
    • /
    • pp.135-144
    • /
    • 2001
  • This study was performed to measure airborne dimethylformamide(DMF), methyl ethyl ketone(MEK) and toluene and their urinary metabolites concentrations and to determine the relationship between airborne and urinary concentration. Airborne samples and their urinary metabolites were measured 98 male workers who work for 8 synthetic leather factories in a portion of Kyoung-In area. Urine samples were collected at end-of-shift to estimate the exposure levels. 1. The concentration of airborne DMF by process was 8.81 ppm for wet-mixing, 15.05 ppm for wet-coating, 6.03 ppm for dry-mixing, 5.58 ppm for dry-coating, 5.37 ppm for printing, and 9.03 ppm for total. There was statistically significant difference by process. Urinary NMF concentrations of wet-mixing, wet-coating, dry-mixing, dry-coating and printing were $90.55mg/{\ell}$, $79.80mg/{\ell}$, $39.86mg/{\ell}$, $25.23mg/{\ell}$, and $38.15mg/{\ell}$, respectively, and total geometric mean was $56.24mg/{\ell}$. There was significant difference by process. 2. The concentration of airborne MEK by process was 1.89 ppm for wet-mixing, 1.96 ppm for wet-coating, 10.33 ppm for dry-mixing, 29.24 ppm for dry-coating, 14.98 ppm for printing, and 4.87 ppm for total. There was statistically significant difference by process. Urinary MEK concentrations of wetmixing, wet-coating, dry-mixing, dry-coating and printing were $0.93mg/{\ell}$, $0.70mg/{\ell}$, $3.29mg/{\ell}$, $3.29mg/{\ell}$, and $1.06mg/{\ell}$, respectively, and total geometric mean was $1.25mg/{\ell}$. There was statistically significant difference by process. Urinary MEK 3. The concentration of airborne toluene by process was 0.35ppm for wet-mixing, 0.42ppm for wet-coating, 2.95ppm for dry-mixing, 11.67ppm for dry-coating, 4.88ppm for printing, 1.24ppm for total. There was statistically significant difference by process. Urinary hippuric acid concentrations of wet-mixing, wet-coating, dry-mixing, dry-coating and printing were 0.24g/g creatinine, 0.21g/g creatinine, 0.34g/g creatinine, 0.52g/g creatinine, and 0.29g/g creatinine, respctively and total geometric mean was 0.28g/g creatinine. There was statistically significant difference by process. 4. No. of exceeded KPEL was 40 workers(40.8%) for DMF(10ppm), 1 worker(1.0%) for MEK(200ppm), and no worker for toluene(100ppm). No. of exceeded KBEI was 62 workers(63.3%) for urinary NMF($40mg/{\ell}$), 29 workers(29.6%) for urinary MEK, 1 worker(1.0%) for urinary hippuric acid. 5. The regression equations were Log(NMF)=0.4094*Log(DMF)+1.3587(r=0.4516) for DMF, Log(MEKU)=0.1859*Log(MEK)-0.0324(r=0.3303) for MEK, Log(HA)=0.2106*Log(Toluene)-0.5685(r=0.4497) for toluene. Synthetic leather factory workers expose to 3 kinds of organic solvents which are DMF, MEK and toluene. Their urinary NMF and MEK levels were higher than their concentration levels through respiratory. It seems that the urinary levels were affected skin absorption for working habit and alcohol intake.

  • PDF

유전자 재조합 B형간염 백신의 10세이하 소아에서의 면역원성 및 안전성 (Immunogenicity and Safety of Recombinant Hepatitis B Vaccine(HG-IIR) in Healthy Infants and Children)

  • 김명아;최은하;장미숙;동은실;장성희;안영민;윤희상;손영모
    • Pediatric Infection and Vaccine
    • /
    • 제4권1호
    • /
    • pp.106-115
    • /
    • 1997
  • 목 적 : B형 간염 바이러스 보균자가 많은 우리 나라에서는 모든 신생아에게 B형 간염에 대한 능동면역이 시행되고 있다. 혈장 백신은 공급원에 한계가 있고 전염성 질환이 전파될 가능성이 있으며 값이 비싸다는 문제점이 있어 이와는 다른 유전자 재조합 공법으로 생산된 HG-II$^{(R)}$백신의 면역원성과 안전성을 조사하고 BCG 선행군과 그렇지 않은 군에서의 면역원성을 비교하고자 본 연구를 시행하였다. 방 법 : 1995년 4월부터 1996년 6월까지 경상대학병원(Group A), 지방공사 강남병원 (Group B)과 영동 세브란스병원(Group C)에서 10세이하의 소아를 대상으로 하여 유전자 재조합 B형간염 백신(HG-II$^{(R)}$)$10{\mu}g$의 양을 0, 1, 6개월 접종 방식으로 3회 근주 하였다. 4군는 BCG를 간염 2차 접종하기 1주전에, B군은 1주후에 접종하였다. C군에서는 두가지 예방접종의 선후관계를 알 수 없었다. 3회 접종후 1개월에 채혈하여 anti-HBs Ab를 측정하였으며 부작용을 조사하였다. 결 과 : 1) 총 114례중 신생아는 104례였으며 이 중 55례는 간염 2차 접종하기 1주전에 BCG를 접종하였고 43례는 간염 2차 접종후에 BCG를 접종하였으며, 6례는 선후관계를 알 수 없었다. 2) 항체양전율은 99.1%였고 기하 평균 항체가는 131.2mIU/ml였다. 3) BCG를 간염 2차 접종하기 1주전에 접종한 군과 1주후에 접종한 군에서의 기하 평균 항체 가는 각각 105.5mIU/ml, 162.8mIU/ml였다(p<0.025). 4) 부작용은 국소 반응이 1.4%, 전신 반응이 7.8%였다. 결 론 : 유전자 재조합 간염 백신은 부작용이 적고 면역원성이 우수하였다. 간염 2차 접종 전에 BCG를 접종한 군에서의 기하 평균 항체가가 낮게 관찰된 바 향후 이에 대한 연구가 더 필요할 것으로 사료된다.

  • PDF

일부 육용 양계 농업인의 유기먼지와 암모니아 노출에 관한 연구 (A Studs on Exposure to Organic Dust and Ammonia in Poultry Confinement Buildings)

  • 신철임;이경숙;김경란;강태선;백남원
    • 농촌의학ㆍ지역보건
    • /
    • 제29권2호
    • /
    • pp.303-314
    • /
    • 2004
  • 본 연구대상의 작업특성을 조사한 결과 일년에 45회 정도 닭을 들여와 사육하였고, 양계업 종사년수는 최소 2년에서 최고 12년이었으며, 평균 종사 년수는 약 8년이었다. 닭을 사육하는 기간에는 일주일 내내 작업을 했고, 하루에 평균 6.3시간을 양계와 관련된 작업을 하며, 양계장 안에서 보내는 시간은 평균 3.3시간이었다. 14가지로 분류한 양계작업 중에서 닭의 입 출하와 분뇨처리는 외부인력과 함께 하거나, 외부인력에 맡기고 있었고, 이를 제외한 대부분의 일을 부부가 함께 하는 편이었다. 양계장의 사료 급여와 급수 시설은 자동시스템이었고, 환기창의 조절은 윈치커튼을 이용한 반자동 시스템이었다. 양계장의 환기는 겨울에는 강제환기를, 그 외 계절에는 자연환기 시스템을 사용하고 있었다. 계사의 바닥 재료는 왕겨를 사용하고 있었으며, 닭을 입하하기 전에 깔아서 출하한 다음에 제거하고 있었다. 양계장 내부애사 측정한 총 먼지와 호흡성 먼지의 지역시료 농도는 각각 평균 4.0mg/$m^3$(Range 3.16.8mg/$m^3$). 0.9mg/$m^3$(Range 0.41.8mg/$m^3$)였으며 호흡성 먼지의 개인노출량은 평균1.4mg/$m^3$(LOD미만 7.8mg/$m^3$)로 나타났다. 암모니아는 지역시료에서 평균 23.3ppm(Range 14.542.1ppm)이 측정되었고 개인노출량은 평균 22.2ppm(13.639.9ppm)으로 나타났다. 먼지의 지역시료 측정결과에서 총먼지에 대한 호흡성 먼지의 비율이 946%로 나타났고 호흡성 먼지 개인노출농도는 6개 농가 중 2개 농가의 개인노출량은 미국산업위생전문가협의회 (American Conference of Governmental Industrial Hygienist: ACGIH)의 노출기준치인3mg/$m^3$ 초과하였다(5.5mg/$m^3$, 7.8mg/$m^3$). 암모니아 개인노출농도 평균은 22.2ppm으로 ACGIH (시간가중)노출기준인 25ppm에 근접하였고, 34.2ppm, 39.9ppm 등 단시간노출기준(STEL) 35ppm과 비슷하거나 넘는 경우가 있어 매우 위험한 상황임을 알 수 있었다. 뿐만 아니라 양계장안에서 작업 중에 노출되는 먼지 또한 일반적인 호흡성먼지 보다 생물활성이 높은 유기먼지라는 점 등을 감안한다면 양계농업인의 건강영향은 매우 우려되는 바, 향후 의학적 검진이 병행되는 종합적인 조사가 필요할 것으로 판단된다.

  • PDF