• 제목/요약/키워드: Visibility Range

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조도와 글자 크기에 따른 가시거리 측정과 예상 (Measurement and Forecast of the Visibility Range according to Illuminance and the Character Sizes)

  • 김태현
    • 한국산학기술학회논문지
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    • 제15권1호
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    • pp.425-429
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    • 2014
  • 가시거리는 무엇인지 정확히 보이는 거리로 정의되며 이는 조도, 글자 크기와 시력 등에 따라 달라진다. 본 논문에서는 4가지 글자 크기와 3가지 조도에 대해서 약 120명의 학생들을 대상으로 교실에서 가시거리를 측정하였다. 측정하지 않은 조도에 대한 가시거리를 예상하기 위해서 최소 제곱 근사 이론을 적용하여 조도가 독립변수이고 가시거리가 종속변수인 함수를 만들었다. 조도가 많이 변해도 가시거리는 조금 밖에 변하지 않으므로 상용로그함수를 이용하여 글자 크기 4가지 각각에 대해서 함수를 만들었다. 만들어진 함수의 값과 측정값과의 오차가 매우 적으므로 함수가 잘 만들어졌음을 보였다.

글자 크기와 조도의 변화에 의한 가시거리 측정과 예상 (Measurement and Prediction of the Visibility Range by the Variations of the Character Sizes and Illuminance)

  • 김태현
    • 한국산학기술학회논문지
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    • 제16권12호
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    • pp.8222-8227
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    • 2015
  • 가시거리는 볼 수 있는 거리로 정의되며, 이는 글자 크기, 조도 등에 따라 바뀐다. 글자 크기와 조도를 결정할 때 가시거리는 중요한 참고 자료가 될 수 있다. 따라서, 본 논문에서는 가시거리 측정과 예상의 2가지 연구를 하였다. 3가지 글자 크기와 3가지 조도에 대해서 약 120명의 학생에 대해서 가시거리를 측정했다. 측정하지 않은 조도에 대한 가시거리를 예상하기 위해서 독립변수가 조도이고, 종속변수가 가시거리인 함수를 제안하였다. 가시거리는 조도에 대해서 많이 바뀌지 않으므로 분수 함수를 제안하였다. 분수 함수에는 결정해야 할 3개의 변수-k,m,n-가 있다.측정한 가시거리 값들을 근거로 이 3개의 변수의 값들을 정하였다. 3개의 조도에 대해서 가시거리를 측정했으므로 세 개의 k들을 계산할 수 있다. 본 논문에서는 이 3개의 k값들의 분산이 가장 작은 경우를 선택하여 이 경우의 3개의 변수-k,m,n-의 값들을 선택하였다. 3개의 글자 크기에 대해서 각각 다른 3개의 분수 함수를 제안하였다. 제안한 함수와 측정한 자료의 차이가 적으므로 제안한 함수가 정확함을 증명하였다.

Forward Scattering Meter 측정에 의한 부산의 하계 시정 특성 (The Characteristics of Visibility Measured by Forward Scattering Meter on Summertime in Pusan)

  • 김유근
    • 한국환경과학회지
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    • 제9권5호
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    • pp.385-388
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    • 2000
  • Visibility reduction is a barometer of air pollution which people can notice easily. First of all we need to measure quantified visibility continuously in order to examine visibility reduction. Prevailing visibility is not practical to measure visibility depending on observer's expertness. Scattering visibility using Forward Scattering Meter(Belfort Visibility Sensor 6230) has been measured at Kwangan-Dong in Pusan and analysed since July 1998. According to the analysis the correlation coefficient(R) between prevailing visibility and scattering visibility was 0.7235. The visibility appeared that each frequency of poor visibility(under 6km) and good visibility(over 25km) was 10.6%, 9.7% on summertime in Pusan and the visibility range from 10km to 20km ranked high frequency as a half of whole ranges. The order of correlation coefficients between visibility an air pollutants are ranking CO. PM10 and NO2 that values are 0.5878, 0.5369,l 0.5284 respectively. In meteorolgical factor the case of poor visibility presented more weakly wind speed and higher relative humidity than the case of good visibility. The correlation coefficient between calculated visibility of multiple linear regression model and observed visibility was 0.7215. But the trend of calculated and observed visibility variation was similar with the exception of several good visibility cases.

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거대 점 오염원의 플룸에 의한 시정 장애 효과 연구 (A Study on Visibility Impairment Impact of the Plume from a Vast Point Source)

  • 배주현;김유근
    • 한국대기환경학회지
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    • 제15권5호
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    • pp.599-611
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    • 1999
  • Now that the plume of point source was suspected to have strong impact on visibility impairment in Pusan, we evaluated visibility impairment impact of the pulme from Pusan Thermo Electric Power Plant in Pusan. Level-1 and-2 analyses were carried out using VISCREEN(Visual Impact Screen model). The emission rates for this Pusan Thermo Electric Power Plant was projected to be 116g/s of nitrogen oxides(as $NO_2$). The source fails the level-1 test with a Plume perceptibility(ΔE) of 30, nearly 15 times the screeing threshold. To characterize worstcase meteorological conditions for level-2 screening, we obtained meteorological data from Mar., 1996 to Feb., 1997 of Pusan Thermo Electric Power Plant. The source fails the level-2 test with a ΔE of 17, nearly 8.5 times the screening threshold. These analyses indicated that adverse visibility impairment could not be ruled out. Therefore a Level-3 analysis was performed using PLUVUE II(Plume Visibility model). As a result, maximum reduction of visual range for 0900LST in winter was 0.9%. Visual impact of the plume from vast point source was judged to be considerable in terms of background visibility of urban area.

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시정장애현상 원인과 그 규명방법 : 수도권 지역의 시정장애현상 연구를 위하여 (Cause and Verification of Visibility Impairment Phenomenon Related to Seoul Area Visibility Study)

  • 백남준;김태오;김용표;문길주
    • 한국대기환경학회지
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    • 제10권1호
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    • pp.1-23
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    • 1994
  • Visibility impairment phenomenon due to various air pollutants is a highly complex problem To understand this problem in Seoul, (1) theoretical background of visibility impairment; (2) methods to quantify visual range and to assess contribution of each air pollutant to the visibility impairment problem; and (3) previous field measurements and modeling studies, both in Korea and abroad, are critically reviewed.

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서울과 춘천의 장기간 시정 변화경향 (Long-term Trends of Visibility in Seoul and Chunchon)

  • 이종범;김용국;백복행
    • 한국대기환경학회지
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    • 제12권4호
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    • pp.473-478
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    • 1996
  • Using data observed from 1966 to 1994, long-term trends of visibility at 15:00 in Seoul and Chunchon were analyzed. Annual average visibility in Seoul has been decreased continuously. In particular, annual number of days for visibility more than 15km was remarkably reduced since 1980. Also, the trend of the visibility in Chunchon was similar to that of Seoul. But the variations were small to compare with Seoul. Long-term trends of relative humidity (RH) and specific humidity (q) at 15:00 in Seoul have been slightly decreased. Cumulative frequency distributions of visibility for ranges of RH (0 $\sim 50%, 50 \sim 60%, 60 \sim 70%, 70 \sim 80%, 80 \sim 90%, 90 \sim 100%$) at 15:00 in Seoul and Chunchon were generally decreased during the second period (1984 $\sim$ 1994) as compared with the first period (1973 $\sim$ 1983), except for the range of 90 to 100% RH. Despite of decreasing phenomena of RH, characteristics of urban climates in Seoul, visibility degraded due to an increase of air pollution.

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Visibility Impairment by Atmospheric Fine Particles in an Urban Area

  • Kim, Young J.;Kim, Kyung W.
    • Journal of Korean Society for Atmospheric Environment
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    • 제19권E3호
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    • pp.99-120
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    • 2003
  • Visibility impairment in an urban area is mainly caused by airborne fine particulate matters. Visibility in a clean air environment is more sensitive to the change of PM$_{2.5}$ particle concentrations. However, a proportionally larger reduction in fine particle concentration is needed to achieve a small increment of visibility improvement in polluted areas. Continuous optical monitoring of atmospheric visibility and extensive aerosol measurements have been made in the urban atmosphere of Kwangju, Korea. The mean for fine particulate mass from 1999 to 2002 at Kwangju was measured to be 23.6$\pm$20.3 $\mu\textrm{g}$/㎥. The daily average seasonal visual range was measured to be 13.1, 9.2, 11.0, and 13.9 km in spring, summer, fall, and winter, respectively. The mean light extinction budgets by sulfate, nitrate, organic carbon, and elemental carbon aerosol were observed to be 27, 14, 22, and 12%, respectively. It is highly recommended that a new visibility standard and/or a fine particle standard be established in order to protect the health and welfare of general public. Much more work needs to be done in visibility studies, including long-term monitoring of visibility, improvement of visibility models, and formulating integrated strategies for managing fine particles to mitigate the visibility impairment and climate change.e.

1980-1993년 기간의 서울의 시정 추이 (The Trend of Visibility Variation of Seoul during 1980-1993)

  • 박세옥;백남준;김용표;문길주;김영성
    • 한국대기환경학회지
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    • 제10권3호
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    • pp.203-208
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    • 1994
  • The trend of visibility variation of Seoul during 1980-1993 is analyzed. Annual average visibility has been decreased during the 1980s except 1988 and 1989 but not decreasing during the early 1990s. Also, the number of days with haze during 1983-1993 did not increase. Mixing height is deemed to be a dominant factor determining visibility. During the period, the difference between the average visibility at 6 p.m and 9 a.m decreased with the average visual range at 9 a.m slightly increased. Thus there is possibility that the effect of Photochemcial reactions becomes noticeable. The number of vehicles and the concentration of criteria air pollutants on the trend of visibility variation of Seoul would not be directly related to the variation of visibility.

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서울지역의 시정 장애 요인에 관한 연구 (On the Origin of Visibility Degradation in Seoul)

  • 윤순창;이강웅
    • 한국대기환경학회지
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    • 제14권3호
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    • pp.229-236
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    • 1998
  • Visibility is a good indicator of comprehensive alto quality. The prevailing visibility in Seoul is no better than the past although the average concentration of SO2 and TSP (total suspended particulate) has decreased quite significantly in the past decade, owing to the government efforts to reduce the emission. Then, a question arises why visibility has not been improved. In order to answer this question we have investigated which components of air pollutants are most responsible for the visibility degradation in Seoul. Analysis on the visibility vs the aerosol sixte distribution measured by an optical particle counter shows that the particles of the size interval between 0.5mm and 2.5mm are most responsible for the visibility degradation. Among the criteria air Pollutants, NOB concentration is found to be moot responsible, rather than PM10. ton analysis of the particulate collected by a high volume sampler shows that the nitrate component increases more significantly than other ions when visibility becomes very poor. Therefore, we conclude that the major causes of visibility degradation in Seoul are the increase of NOB, nitrates and the particles of the size range between 0.5mm and 2.5mm.

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