DOI QR코드

DOI QR Code

미술대학 조소작업 중 발생하는 분진 및 소음에 대한 노출평가

Exposure Assessment to Particulates and Noise among Sculptors at a College of Fine Art

  • 조현우 (서울대학교 보건대학원 환경보건학과, 보건환경연구소) ;
  • 윤충식 (서울대학교 보건대학원 환경보건학과, 보건환경연구소) ;
  • 함승헌 (서울대학교 보건대학원 환경보건학과, 보건환경연구소) ;
  • 이임규 (서울대학교 보건대학원 환경보건학과, 보건환경연구소) ;
  • 박지훈 (서울대학교 보건대학원 환경보건학과, 보건환경연구소) ;
  • 박동진 (서울대학교 보건대학원 환경보건학과, 보건환경연구소) ;
  • 정진호 (서울대학교 환경안전원) ;
  • 염종수 (서울대학교 환경안전원) ;
  • 서규진 (서울대학교 환경안전원)
  • Cho, Hyun-Woo (Department of Environmental Health, Graduate School of Public Health and Institute of Health and Environment, Seoul National University) ;
  • Yoon, Chung-Sik (Department of Environmental Health, Graduate School of Public Health and Institute of Health and Environment, Seoul National University) ;
  • Ham, Seung-Hon (Department of Environmental Health, Graduate School of Public Health and Institute of Health and Environment, Seoul National University) ;
  • Lee, Lim-Kyu (Department of Environmental Health, Graduate School of Public Health and Institute of Health and Environment, Seoul National University) ;
  • Park, Ji-Hoon (Department of Environmental Health, Graduate School of Public Health and Institute of Health and Environment, Seoul National University) ;
  • Park, Dong-Jin (Department of Environmental Health, Graduate School of Public Health and Institute of Health and Environment, Seoul National University) ;
  • Chung, Jin-Ho (Institute of Environmental Protection and Safety, Seoul National University) ;
  • Yeom, Jong-Soo (Institute of Environmental Protection and Safety, Seoul National University) ;
  • Seo, Kyu-Jin (Institute of Environmental Protection and Safety, Seoul National University)
  • 투고 : 2011.07.26
  • 심사 : 2011.08.19
  • 발행 : 2011.08.31

초록

Objectives: A great number of hazardous agents can be emitted from various types of art-creation in a fine arts college, but little data on exposure assessment has been published. A variety of processes encompassing toxic or non-toxic materials, tools, and components are involved in a sculptor work at a fine art college. The aim of this study was to assess exposure levels to particulates and noise during sculpture classes in a college of fine arts. Methods: Students in sculpture classes participated in this study. Mass, number, and surface area concentrations of particulates, noise level, temperature and relative humidity were monitored by both personal and area sampling during the tasks of metal, wood, and stone sculpting. Results: The number and surface concentration of particulates was the highest in the task of wood sculpting, followed by metal and stone work. The mass concentration of particulates was the highest in stone sculpting (personal GM 3.0 mg/$m^3$, GSD 3.0), followed by wood (personal GM 1.5 mg/$m^3$, GSD 1.8) and metal work (personal GM 0.95 mg/$m^3$, GSD 1.51) in that order. Occupational exposure limits (OEL) for particulates depends on the type of particulate. For wood dust, 86% (six subjects) of the personal samples and all area samples exceeded the Korean OEL for wood dust (1 mg/$m^3$), while 20% (two subjects) among stone sculpting students were exposed above the Korean OEL (10 mg/$m^3$). In contrast, metal sculpting did not exceed the OEL (5 mg/$m^3$). For noise level, metal sculpting students (Leq 95.1 dB(A) in the morning, 85.3 dB(A) in the afternoon) were exposed the most, followed by stone sculpting (88.3 dB(A)), and wood sculpting (84.8 dB(A)) in that order. Compared with the 90 dB(A) of the Korean OEL and 85 dB(A) of the American Conference of Governmental Industrial Hygienists' threshold limit value (ACGIH-TLV) for noise, 100% of the subjects (five subjects) and area samples during metal sculpting in the morning session exceeded both OELs, but only three subjects (60%) exceeded the ACGIH-TLV in the afternoon session. For stone sculpting, 50% (one subject) and 100% (two subjects) exceeded the Korean OEL and ACGIH-TLV, respectively, but the area sample did not exceed either OEL. During wood sculpting, two subjects (40%) exceeded ACGIH TLV. Conclusions: This work evaluated the sculptors' exposure to particulate matter and noise in fine art college, and revealed a poor working environment for the participating students. Effective measures should be supplemented by the administration of colleges.

키워드

참고문헌

  1. Ministry of education, science and technology. The entrance quota of all colleges in Korea, 2010. Available: http://www.mest.go.kr/web/1114/ko/board/view. do?bbsId=153&boardSeq=15438 [accessed 25 July 2011].
  2. Siedlecki JT. Potential health hazards of sculptors' materials. Pergamon Press. 1971; 4: 381-384.
  3. Deam RT, Simpson SW, Haidar J. A semi-empirical model of the fume formation from gas metal arc welding. J Phys D Appl Phys. 2000; 33: 1393-1402. https://doi.org/10.1088/0022-3727/33/11/320
  4. Vincent JH, Clement CF. Ultrafine particles in workplace atmospheres. Phil Trans R Soc Lond A. 2000; 358: 2673-2682. https://doi.org/10.1098/rsta.2000.0676
  5. Siedlecki JT. Potential health hazards of materials used by artists and sculptors. Art Education. 1972; 25: 21-26.
  6. Hagaman S. Art hazards: concerns of the art teacher. Art Education. 1986; 39(3): 44-46. https://doi.org/10.2307/3192957
  7. Niemeyer S, Rich W. Arts and crafts can be hazardous. Historical materials from university of nebraska-lincoln extension NF93-125; 1993.
  8. Moroni B, Viti C. Grain size, chemistry, and structure of fine and ultrafine particles in stainless steel welding fumes. J Aerosol Sci. 2009; 40(11): 938- 949. https://doi.org/10.1016/j.jaerosci.2009.08.004
  9. Park K. Toxicity of nanomaterials and strategy of risk assessment. J Environ Toxicol. 2005; 20(4): 259-271.
  10. Ahmed HO, Dennis JH, Badran O, Ismail M, Ballal SG, Ashoor A, et al. Occupational noise exposure and hearing loss of workers in two plants in eastern Saudi arabia. Ann Occup Hyg. 2001; 45(5): 371-380. https://doi.org/10.1093/annhyg/45.5.371
  11. Kim WT, Kim DH, Lee CK, Ahn JH, Lee CH, Kim HD, et al. Hearing asymmetry among occupationally noise-exposed workers. J Korean Soc Occup Environ Hyg. 2007; 17(2): 153-159.
  12. Shamssain MH. Pulmonary function and symptoms in workers exposed to wood dust. Thorax. 1992; 47: 84-87. https://doi.org/10.1136/thx.47.2.84
  13. Ahman M, Soderman E, Cynkier I, Birgitta KH. Work-related respiratory problems in industrial arts teachers. Int Arch Occup Environ Health. 1995; 67: 111-118. https://doi.org/10.1007/BF00572234
  14. Parks CG, Conrad K, Cooper GS. Occupational exposure to crystalline silica and autoimmune disease. Environmental Health Perspectives. 1999; 107(5): 793-802. https://doi.org/10.1289/ehp.99107s5793
  15. Lumens MEGL, Spee T. Determinants of exposure to respirable quartz dust in the construction industry. Ann Occup Hyg. 2001; 45(7): 585-595. https://doi.org/10.1093/annhyg/45.7.585
  16. Harris MK, Ewing WM, Longo W, EdPasquale C, Mount MD, Hatfield R, et al. Manganese exposures during shielded metal arc welding (SMAW) in an enclosed space. J Occup Environ Hyg. 2005; 2: 375-382. https://doi.org/10.1080/15459620591007736
  17. Meeker JD, Susi P, Flynn MR. Manganese and welding fume exposure and control in construction. J Occup Environ Hyg. 2007; 4: 943-951. https://doi.org/10.1080/15459620701718867
  18. Dasch J, D'Arcy J. Physical and chemical characterization of airborne particles from welding operations in automotive plants. J Occup Environ Hyg. 2008; 5: 444-454. https://doi.org/10.1080/15459620802122720
  19. Schlunssen V, Vinzents PS, Mikkelsen AB, Schaumburg I. Wood dust exposure in the Danish furniture industry using conventional and passive monitors. Ann Occup Hyg. 2001; 45(2): 157-164. https://doi.org/10.1093/annhyg/45.2.157
  20. Yamanaka MW, Guidotti TL, Koehncke N, Taylor FM, Taylor C, Harman L. Wood dust levels in Alberta sawmills. Archives of Environmental & Occupational Health. 2009; 64(4): 270-277. https://doi.org/10.1080/19338240903338247
  21. Lee T, Harper M, Slaven JE, Lee KY, Rando RJ, Maples EH. Wood dust sampling: field evaluation of personal samplers when large particles are present. Ann Occup Hyg. 2011; 55(2): 180-191. https://doi.org/10.1093/annhyg/meq075
  22. Junttila S, Tossavainen A, Hartikainen T, Harma P, Korhonen K, Suominen V, et al. Airborne mineral dust at nine crushed rock plants in Finland. Appl Occup Environ Hyg. 1997; 12(12): 882-886. https://doi.org/10.1080/1047322X.1997.10390623
  23. Fulekar MH. Occupational exposure to dust in quartz manufacturing industry. Ann Occup Hyg. 1999; 43(4): 269-273. https://doi.org/10.1093/annhyg/43.4.269
  24. Flanagan ME, Seixas N, Majar M, Camp J, Morgan M. Silica dust exposures during selected construction activities. AIHA J. 2003; 64: 319-328. https://doi.org/10.1080/15428110308984823
  25. Hattis D. Occupational noise sources and exposures in construction industries. Human and Ecological Risk Assessment. 1998; 4(6): 1417-1441. https://doi.org/10.1080/10807039891284758
  26. Landen D, Wilkins S, Stephenson M, McWilliams L. Noise exposure and hearing loss among sand and gravel miners. J Occup Environ Hyg. 2004; 1: 532- 541. https://doi.org/10.1080/15459620490476503
  27. Gupta S, McCann M, Harrison J. Health hazards in the arts and crafts. Leonardo. 1991; 24(5): 569-572. https://doi.org/10.2307/1575662
  28. McCann MF. Occupational and environmental hazards in art. Environmental Research. 1992; 59: 139- 144. https://doi.org/10.1016/S0013-9351(05)80233-6
  29. Hamilton S. Health hazards and safety tips for artists. Canadian Artists Representation/Le Front Des Artistes Canadians (CARFAC), 2000.
  30. U.S. Consumer Product Safety Commission (CPSC). Art and craft safety guide. Bethesda, MD 20814. Available from: http://www.cpsc.gov/cpscpub/ pubs/5015.pdf [accessed 25 July 2011].
  31. Park JY, Ramachandran G, Raynor PC, Eberly LE, Olson G Jr. Comparison exposure zones by different exposure metrics using statistical parameters: contrast and precision. Ann Occup Hyg. 2010; 54(7): 799-812. https://doi.org/10.1093/annhyg/meq043
  32. Buonanno G, Morawska L, Stabile L. Exposure to welding particles in automotive plants. J Aerosol Sci. 2011; 42: 295-304. https://doi.org/10.1016/j.jaerosci.2011.02.003
  33. Methner M, Hodson L, Dames A, Geraci C. Nanoparticle emission assessment technique (NEAT) for the identification and measurement of potential inhalation exposure to engineered nanomaterials- Part B: results from 12 field studies. J Occup Environ Hyg. 2010; 7: 163-176. https://doi.org/10.1080/15459620903508066
  34. Demange M, Gorner P, Elcabache J-M, Wrobel R. Field comparison of 37-mm closed-face cassettes and IOM samplers. Appl Occup Environ Hyg. 2002; 17(2): 200-208. https://doi.org/10.1080/104732202753438289