DOI QR코드

DOI QR Code

Characteristics of Ammonia in Alkaline Stabilization Facility of Sludge from Sewage Treatment Plant

하수처리오니 알칼리 안정화 처리시설에서의 암모니아 발생특성

  • Kim, Yong-Jun (Resource Recirculation Research Division, National Institute of Environmental Research) ;
  • Chung, David (Resource Recirculation Research Division, National Institute of Environmental Research) ;
  • Jeong, Mi-Jeong (Resource Recirculation Research Division, National Institute of Environmental Research) ;
  • Yoo, Hye-Young (Resource Recirculation Research Division, National Institute of Environmental Research) ;
  • Yoon, Cheol-Woo (Resource Recirculation Research Division, National Institute of Environmental Research) ;
  • Shin, Sun-Kyoung (Resource Recirculation Research Division, National Institute of Environmental Research)
  • 김용준 (국립환경과학원 자원순환연구과) ;
  • 정다위 (국립환경과학원 자원순환연구과) ;
  • 정미정 (국립환경과학원 자원순환연구과) ;
  • 유혜영 (국립환경과학원 자원순환연구과) ;
  • 윤철우 (국립환경과학원 자원순환연구과) ;
  • 신선경 (국립환경과학원 자원순환연구과)
  • Received : 2016.06.28
  • Accepted : 2016.07.28
  • Published : 2016.09.30

Abstract

The characteristics of ammonia generated from alkaline stabilization facilities was investigated which are for organic sewage sludge from wastewater treatment plants. The highest concentration of ammonia was found in mixing and curing process in alkaline stabilization facility and ammonia mainly showed a range of 87.78 ppm($66.62mg/m^3$) to 1,933 ppm($1,467.01mg/m^3$) by detection tube. This is presumed to occur because nitrogen oxides are converted into ammonia as the sewage sludge is mixed with lime. In some facilities, hydrogen sulfide and methyl mercaptan were detected in relatively high concentrations, but odor materials except ammonia were not detected in most of the facilities. The concentration of ammonia caused by process was generally high in the order of "mixing > curing > output > storage > drying > input." It was found that odor compounds are removed by wet absorption using sulfuric acid and sodium hypochlorite in the 5 alkaline stabilization facilities currently in operation. Each facility was designed to meet the concentration of after-treatment emission in 1 ppm($0.76mg/m^3$), 50 ppm($37.95mg/m^3$) or 100 ppm($75.89mg/m^3$), but no facility satisfied the design standard for their emssion limit. In case of ammonia, some workplaces in alkaline stabilization facilities exceeded the exposure limits established by the Ministry of Labor. It appears that proper ventilation should be provided for the safety of workers in future. No odor compound including ammonia was found by detection tubes in the border of the facilities, but trace amounts of odor compounds are expected to exist, given the current operational status of facilities.

본 연구는 하수처리시설의 유기성슬러지가 알칼리 안정화 처리시설을 거쳐 발생되는 암모니아의 특성을 조사하였다. 암모니아 검지관을 통해 알칼리 안정화 처리시설의 혼합 및 양생 공정에서 87.78 ppm($66.62mg/m^3$) ~ 1,933 ppm($1,467.01mg/m^3$) 으로 높은 농도의 암모니아가 검출 되었다. 이는 하수처리오니의 질소산화물이 생석회와 혼합되며 암모니아로 변환되는 것으로 예상된다. 일부 시설에서는 황화수소, 메틸메르캅단이 비교적 높은 농도로 검출되었으나, 대부분의 시설에서는 암모니아를 제외한 악취 물질은 검출되지 않았다. 공정 중 암모니아의 농도는 일반적으로 혼합 > 양생 > 반출 > 저장 > 건조 > 입고 순으로 높게 나타났다. 현재 운영 중인 5개 알칼리 안정화 처리시설에서 발생된 악취 물질들은 황산과 차아염소산 등을 사용하여 습식처리하는 것으로 조사되었다. 각 시설은 1 ppm($0.76mg/m^3$), 50 ppm($37.95mg/m^3$) 또는 100 ppm($75.89mg/m^3$)으로 방출되도록 설계되었으나 설계 기준을 만족하지 못하는 것으로 나타났다. 암모니아의 경우, 일부 알칼리 안정화 처리시설은 노동부가 정한 노출기준을 초과하는 것으로 조사되었다. 이것은 향후 근로자의 안전을 위해 적절한 환기가 필요함을 의미하고 있다. 또한, 암모니아를 포함한 악취물질이 시설의 부지경계선에서 검지관으로 검출되지 않았으나, 현재의 운전상태로 볼 때, 미량의 악취물질이 존재할 것으로 판단된다.

Keywords

References

  1. Ministry of Environment, "Statistics of Sewerage 2010", (2011).
  2. Nam, Y. W. and Han, K. S., "A Study on the Present State and Improvement Plan of Domestic Sewage Sludge Treatment", Journal of Korea Society of Waste Management, 28(1), pp. 103-109. (2011).
  3. Ministry of Environment, "2010 Albaro System", (2011).
  4. Ministry of Oceans and Fisheries, "Regulation of Marine Environment Management", (2012).
  5. Ministry of Environment, "2012 Basic Plan for Disposal of Sewage Sludges by Prohibition of Ocean Dumping", (2012).
  6. Kang, S. J., Lee, C., Kim, H. B., An, D. G., Youn, H. C. and Kang, J. S., "Utilization of dried and solidified sewage sludge as daily cover material in waste landfill", Journal of the Korean Society of Civil Engineers, 54(4), pp. 61-68. (2006).
  7. Park, S. C., "Utilization of sewage sludge as cover material in waste landfill", Journal of Korea Organic Resource Recycling Association, 14(1), pp. 88-101. (2006).
  8. National Institute of Environmental Research, "Study on Facility Guideline for Solidification(Alkaline Stabilization) of Sludge from Sewage Treatment Plant", NIER No. 2011-06-1292, (2011).
  9. Hyun, J. H., Jung, B. D. and Kim, M. G., "Utilization of Solidified Sewage Sludge as Daily Cover Material in Landfill", Journal of Korea Society of Waste Management, 24(7), pp. 670-675. (2007).
  10. National Institute of Environmental Research, "Study on Quality Standards of material for Alkaline Stabilization of Sewage Treatment Plant Sludge", NIER No. RP2011-1338, (2011).
  11. Ministry of Environment, "A Study on Improvement for management of Odor Sources", (2001).
  12. Ministry of Employment and Labor, "Exposure Level of Chemicals and Physical Parameters", Notice No. 2013-38, (2011).
  13. Korean Agency for Technology and Standards, "Detector tube type gas measuring instruments, KS I 2218", (2009).
  14. Ministry of Employment and labor, "Notification about assessment of a work environment monitoring and a designated monitoring institution", (2012).
  15. Sa, J. H., Yoon, S. K., Roh, G. H. and Jeon, E. C., "Analysis methods for measurement of ammonia concentration", Journal of Korean Society for Atmospheric Environment, 24(1), pp. 43-54. (2008). https://doi.org/10.5572/KOSAE.2008.24.1.043
  16. Lim, J. J., Kim, H. S. and Kim, S. T., "The study on the realtime evaluation of NH3 absorption efficiency using chemical gas sensor", Journal of Korean Society of Environmental Engineers, 35(4), pp. 233-239. (2013). https://doi.org/10.4491/KSEE.2013.35.4.233
  17. Kim, E. H., Lee, K. S. and CHo, J. K., "Added effects of gypsum on the solidification of sewage sludge cake", Journal of Korean Society of Water & Wastewater, 14(4), pp. 303-310. (2000).
  18. Wikipedia, "Ammonia, Wikipedia The Free Encyclopedia", http://en.wikipedia.org/wiki/Ammonia (assess date: June 3, 2015)
  19. Hwang, Y. W., "Fermentation of sewage sludge, capping the landfill using a solidification process manufacturing technology", Korea Organic Resource Recycling Association, 12(3), pp. 49-60. (2004).
  20. Ministry of environment, "Clean Air Conservation Act [Annex 8]", (2010).
  21. Kim, H. J., Bae, U. S., Oh, C. H., Kim, T. H., Kim, J. B., Ryu, H. R. and Kim, T. H., "A Study on Management Improvement of Deodorization Equipment of Food Waste Treatment Facility", Korean Journal of Odor Research and Engineering, 8(1), pp. 20-30. (2009).
  22. Lee, H. D., Kang, D. J., Lee, M. H., Kang, D. H. and Oh, K. J., "Removal Efficiency of the Deoderization Equipment and Characteristics of Malodor during the Process in Co-treatment of Sewage and Food Waste of Su-young Wastewater Treatment Plant in Busan", CLEAN TECHNOLOGY, 18(4), pp. 379-389. (2012). https://doi.org/10.7464/ksct.2012.18.4.379
  23. Choi, S. D., Kim, J. H., Chang, Y. S., Park, J. B., Lee, S. H. and Yoon, H. T., "Reduction of Odor Emissions from the Field Workplaces at the Pohang Steel Complex using Pyroligneous Liquid", Korean Journal of Odor Research and Engineering, 5(1), pp. 33-39. (2006).
  24. Park, J. T., Kim, Y. D., Ha, S. H., Kim, J. S. and Kim, S. N., "Improvements of IAQ around Coremaking Machines Using CFD", Journal of the Wind Engineering Institute of Korea, 9(2), (2005).
  25. Jeon, J. M., Seo, Y. S., Jeong, M. H., Lee, H. S., Lee, M. D., Han, J. S. and Kang, B. W., "The Emission Characteristics of Odor Compounds from Environment Fundamental Facilities", Korean Journal of Odor Research and Engineering, 9(2), pp. 80-89. (2010).