The Removal of Dioxins and the Formation of 2, 3, 7, 8-TeCDF in Drinking Water Treatment in Japan

정수처리에서의 다이옥신 제거 및 2, 3, 7, 8-TeCDF 생성

  • Kim, Hyun-koo (Department of Environmental Diagnostics Research, National Institute of Environmental)
  • 김현구 (국립환경과학원 환경진단연구부)
  • Received : 2008.08.27
  • Accepted : 2008.10.21
  • Published : 2008.11.30

Abstract

To evaluate homologue patterns and removal efficiency before and after water treatment, the concentrations of dibenzo-p-dioxins (PCDDs), polychlorinated dibenzofurans (PCDFs) and coplanar polychlorinated biphenyls (Co-PCBs) were determined in 122 samples from 42 drinking water treatment plants throughout Japan over a two year period. The mean concentrations and toxic equivalent (TEQ) values of dioxins in raw and treated waters were 60.24 pg/L (0.14 pg-WHO-TEQ/L) and 4.15 pg/L (0.016 pg-WHO-TEQ/L), respectively. The dioxins contribution ratio of drinking water in relation to dioxins tolerable daily intake (TDI, 4 pg-TEQ/kg/day) was 0.016%. The mean TEQ removal rate of dioxins by drinking water treatment was over 88%. However, the mean removal rate of 2, 3, 7, 8-TeCDF (tetrachlorodibenzofuran) by water treatment in the 122 samples was minus 17%. Therefore, to identify which process affected the level of 2, 3, 7, 8-TeCDF, the removal efficiencies at both the advanced and conventional water treatment plants were investigated. For the TEQ removal rate across the processes, the dioxin congeners, TeCDF and non-ortho-PCBs remarkably indicated minus values after chlorination in both the advanced and conventional water treatments plant. From this study, the level of 2, 3, 7, 8-TeCDF was found to be increased as a result of chlorination.

먹는물 처리 전후 다이옥신류의 동족체 패턴 및 제거율을 평가하기 위해서 42개의 일본 정수처리장에서 2년간 122개의 시료를 채취해 dibenzo-p-dioxins (PCDDs), polychlorinated dibenzofurans (PCDFs) 및 coplanar polychlorinated biphenyls (Co-PCBs)를 분석하였다. 다이옥신류의 평균 농도와 독성등가값 (toxic equivalent, TEQ)은 원수와 처리수에서 각각 60.24 pg/L (0.14 pg-WHO-TEQ/L), 4.15 pg/L (0.016 pg-WHO-TEQ/L)였다. 먹는물의 다이옥신류 기여 농도는 일일섭취량 (tolerable daily intake (TDI), 4 pg-TEQ/kg/day)의 0.016%이었다. 정수처리에 의한 다이옥신류의 평균 TEQ 제거율은 88% 이상이었다. 그러나 112개의 샘플에서 2, 3, 7, 8-TeCDF (tetrachlorodibenzofuran)의 농도는 17% 증가하였다. 따라서, 2, 3, 7, 8-TeCDF의 농도에 영향을 미치는 공정을 파악하기 위하여 고도정수처리 및 일반정수처리에서의 제거율을 조사하였다. 다이옥신 동족체(congener)인 TeCDF와 non-ortho-PCB는 고도처리 및 표준정수처리에서 염소소독처리 후 TEQ 농도가 증가함을 보여, 먹는물 중 2, 3, 7, 8-TeCDF 농도는 염소소독처리에 의해 상승한 것으로 밝혀졌다.

Keywords

References

  1. Czuczwa, J. M. and Hites, R. A. (1984). Environmental fate of combustion-generated polychlorinated dioxins and furans. Environ Sci. Technol., 18, pp. 444-450 https://doi.org/10.1021/es00124a010
  2. Japanese Ministry of Health and Welfare (1997). Survey of dioxins from the food (Heisei kyu nendo shokuhin no nakano daikokisin osen jittai chousa)
  3. Japanese Environmental Agency (1999). Environmental Standard Regulation of atmosphere, water and land contamination by dioxins. Notification No. 68 of Japanese Environmental Agency
  4. Kim, H. K., Masaki, H., Matsumura, T., Kamei, T., and Magara, Y. (2002). Removal efficiency and homologue patterns of dioxins in drinking water treatment. Water Research, 36, pp. 4861-4869 https://doi.org/10.1016/S0043-1354(02)00202-6
  5. Luthe, C. E. and Berry, R. M. (1996). The role of dibenzop- dioxin and dibenzofuran precursors in the formation of tetrachlorinated dibenzo-p-dioxins/-furans during bleaching. Chemosphere, 32, pp. 881-891 https://doi.org/10.1016/0045-6535(96)00022-7
  6. Magara, Y., Aizawa, T., Ando, M., Morita, M., Ito, H., Seki, Y., and Mastumura, T. (1999). Determination of low dioxins and PCB's concentration in ambient water using large volume "in situ" pre-concentration system. 19th international Symposium Halogenated Environmental Organic Pollutants POPs 40, pp. 205-210
  7. Marple, L., Brunck, R., and Throop, L. (1986). Water solubility of 2,3,7,8-tetrachlorobenzo-p-dioxin. Environ. Sci. Technol., 20, pp. 180-182 https://doi.org/10.1021/es00144a012
  8. Masunaga, S., Takasuga, T., and Nakanishi, J. (2001). Dioxin and dioxin like PCB impurities in some Japanese agrochemical formulations. Chemosphere, 44, pp. 873-885 https://doi.org/10.1016/S0045-6535(00)00310-6
  9. Morrison, R. T. and Boyd, R. N. (1983). Organic chemistry (4th Eds). Allyn and Bacon, Inc., Boston
  10. Rappe, C. and Buser, H. R. (1989). Chemical and physical properties, analytical methods, sources and environmental levels of halogenated dibenzodioxins and dibenzofurans. In: Halogenated Biphenyls, Terphenyls, Naphthalenes, Dibenzodioxins and Related Products (Kimbrough, R. D. Jensen, A. A. Eds.). Elsevier, Amsterdam, pp. 71-102
  11. Sakurai, T., Suzuki, N., Masunaga, S., and Nakanishi, J. (1998). Origin attribution of polychlorinated dibenzo-pdioxins and dibenzofurans in sediment and soil from a Japanese fresh water lake area through congener-specific data analysis. Chemosphere, 37, pp. 2211-2224 https://doi.org/10.1016/S0045-6535(98)00282-3
  12. Smirnov, A. D., Schecter, A., Papke, O., and Beljak, A. A. (1996). Conclusion from UFA, Russia, drinking water dioxin clean up experiments involving different technologies. Chemosphere, 32, pp. 479-489 https://doi.org/10.1016/0045-6535(95)00235-9
  13. Wenning, R. J., Harris, M. A., Ungs, M. J., Paustenbach, D. J., and Bedbury, H. (1992). Chemometric comparison of polychlorinated dibenzo-p-dioxins and dibenzofurans residues in surficial sediments from Newark Bay, New Jersey and other industrialized waterways. Arch Environ Contam Toxicol., 22, pp. 397-413 https://doi.org/10.1007/BF00212560
  14. WHO (2001). WHO's recommendation concerns maximum tolerable daily intake of dioxins, not salomon. Statement WHO/01