2007, Piran, Slovenia

2007, Piran, Slovenia 2007, Piran, Slovenia

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Environmental Ergonomics XII Igor B. Mekjavic, Stelios N. Kounalakis & Nigel A.S. Taylor (Eds.), © BIOMED, Ljubljana 2007 The present study contributes to a new qualitative and quantitative description of the physical and mental aspects of perceived fatigue. Five dimensions of fatigue have been proposed. To assure the reliability and validity of the five dimensions, further experiments and studies are in progress. REFERENCES Åhsberg, E., 1998. Perceived quality of fatigue during different occupational tasks Development of a questionnaire. International Journal of Industrial Ergonomics, 20:121- 135. Astrand, P. O. And Rodahl, K., 1986.Textbook of Work Physiology. Physiological Bases of Exercise. McGraw-Hill, NewYork. Bartlett F. Psychological criteria of fatigue. In: Floyd W, Welford A, eds. 1953. Symposium on fatigue. London:H.K. Lewis & Co, pp.1-5. Basmajian, J. and De Luca, C., 1985. Muscles Alive. Williams & Wilkins, Baltimore. Bigland-Ritchie, Woods J. 1984. Changes in muscle contractile properties and neural control during human muscular fatigue. Muscle & Nerve 7:669-699. Britton D. Fatigue. In: Yasko J, ed. 1983. Guidelines for cancer care. Reston: Raven Publishing Company, pp. 33-37. Browne R. Fatigue, fact or fiction? In: Floyd W, Welford A, ed. 1953. Symposium on fatigue. London: H.K. Lewis & Co, pp.137-142. Chalder, T., Berelowitz, G., Pawlikowska, T., Watts, L., Wessely, S., Wright, D. and Wallace, E, 1993. Development of a fatigue scale. Journal of Psychosomatic Research, 37: 147- 153. Christensen E. Muscular work and fatigue. In: Rodahl K, Horvath S, ed. 1962. Muscle as a tissue. New York: McGraw-Hill, 176-189. Deeb, M.J. 1999. Muscular fatigue and its effects on weight perception. International Journal of Industrial Ergonomics, 24:223-233. Eidelman D. 1980.Fatigue: Towards an analysis and a unified definition. MedHypoth; 6:517- 526. Gamberale, F., Kjellberg, A., Akerstedt, T. and Johansson, G. 1990. Behavioral and psychophysiological effects of the physical work environment. Scandinavian Journal of Work, Environment and Health, 16: 5-16. Goldmark J. 1912.Fatigue and efficiency. New York: Russell Sage Foundation. Hemingway A. 1953 .The physiological background of fatigue. In: Floyd W, Welford A, eds. Symposium on fatigue. London: H. K. Lewis & Co, pp. 69-75. Kilbom, A., Fysiskt arbete, fysiologisk belastning, In: N. Lundgren, G. Luthman and K. Elgstrand (Eds.), 1987.Mainniskan iarbete. Nordstedts FiSrlag AB, Stockholm, pp.48-92. Melzack, R., 1987. The short-form McGill pain questionnaire. Pain, 30: 191-197. Mital A, Foononi-Fard H, Brown M. 1994. Physical fatigue in high and very high frequency manual materials handling: Perceived exertion and physiological indicators. Hum Factors. 36:219-231. Muscio, B., 1921. Is a fatigue test possible? British Journal of Psychology, 12: 31-46. Piper B. Fatigue. In: Carrieri V, Lindsay A, west C, ed. 1986. Pathophysiological phenomena in nursing: Human responses to illness. Philadelphia: W.B. Sanders & Co, pp.219-234. Roman-Liu, D. Tokarski, T., 2005. Upper limb strength in relation to upper limb posture. International Journal of Industrial Ergonomics, 35: 19–31. Wessely, S, Hotopf M, Sharpe M. 1998. Chronic fatigue and its syndromes. Oxford: Oxford University Press. Yoshitake, H. 1978. Three characteristic patterns of subjective fatigue sysptoms. Ergonomics, 21: 231-233. 570

Working Environment ANTHROPOGENIC IMPACT ON AEROSOL MASS DISTRIBUTION IN CENTRAL INDIA N. K. Jaiswal, K. S. Patel School of Studies in Chemistry, Pt. Ravishankar Shukla University, Raipur, CG, India. Contact person: nitinkjaiswal@hotmail.com The problem of air pollution has attracted special attention in Central India due to tremendous increase in the amount of pollution accompanying the extensive industrialization and urbanization over the last few decades. The highest deposits of minerals and fossil fuels are in Central India. At least 20% of India’s iron ore and 50% its coal reserves are in this region, including rich deposits of bauxite, limestone, dolomite and corundum. In addition, many thermal power plants, steel and metal industries, cement industries, rice and spice processing units are running there. These industries are associated with the production of aerosol particulates, and both fine (PM2.5) and coarse particulates (PM10) can accumulate in the respiratory tract, increasing the risk of numerous adverse health effects. At least 50% of people working in coal mines, thermal and steel plants are suffering with serious respiratory diseases such as bronchitis, asthma, chronic obstructive pulmonary disease, lung cancer and heart diseases, due to exposure to fine particulates generated by high industrial thermal processes. In addition, Bhilai Steel Plant is the biggest unit for iron manufacturing, and it is a major consumer of coal. Furthermore, other high consuming units for coal are the National Thermal Plant Corporation (NTPC) and the Bharat Aluminum Limited Company (BALCO). In the present study, changes in the response of near surface aerosol properties, and their associations with meteorological parameters have been studied during one year in Raipur Chhattisgarh. The seasonal variation of aerosol mass concentration (PM10 and PM2.5) was high in winter and low in the monsoon season. The annual mass concentration of PM10 and PM2.5 ranged from 62-975 and 20-373 µgm -3 , respectively. The RSPM, TSPM levels are also measured in Industrial sites. 571

Working Environment<br />

ANTHROPOGENIC IMPACT ON AEROSOL MASS DISTRIBUTION IN<br />

CENTRAL INDIA<br />

N. K. Jaiswal, K. S. Patel<br />

School of Studies in Chemistry, Pt. Ravishankar Shukla University, Raipur, CG, India.<br />

Contact person: nitinkjaiswal@hotmail.com<br />

The problem of air pollution has attracted special attention in Central India due to tremendous<br />

increase in the amount of pollution accompanying the extensive industrialization and<br />

urbanization over the last few decades. The highest deposits of minerals and fossil fuels are in<br />

Central India. At least 20% of India’s iron ore and 50% its coal reserves are in this region,<br />

including rich deposits of bauxite, limestone, dolomite and corundum. In addition, many<br />

thermal power plants, steel and metal industries, cement industries, rice and spice processing<br />

units are running there. These industries are associated with the production of aerosol<br />

particulates, and both fine (PM2.5) and coarse particulates (PM10) can accumulate in the<br />

respiratory tract, increasing the risk of numerous adverse health effects. At least 50% of<br />

people working in coal mines, thermal and steel plants are suffering with serious respiratory<br />

diseases such as bronchitis, asthma, chronic obstructive pulmonary disease, lung cancer and<br />

heart diseases, due to exposure to fine particulates generated by high industrial thermal<br />

processes. In addition, Bhilai Steel Plant is the biggest unit for iron manufacturing, and it is a<br />

major consumer of coal. Furthermore, other high consuming units for coal are the National<br />

Thermal Plant Corporation (NTPC) and the Bharat Aluminum Limited Company (BALCO).<br />

In the present study, changes in the response of near surface aerosol properties, and their<br />

associations with meteorological parameters have been studied during one year in Raipur<br />

Chhattisgarh. The seasonal variation of aerosol mass concentration (PM10 and PM2.5) was high<br />

in winter and low in the monsoon season. The annual mass concentration of PM10 and PM2.5<br />

ranged from 62-975 and 20-373 µgm -3 , respectively. The RSPM, TSPM levels are also<br />

measured in Industrial sites.<br />

571

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