경남지역 상수 원·정수의 냄새물질 발생 특성 평가
Evaluation of 2-Methyl Isoborneol and Geosmin Concentrations of Source and Tap Water from Water Supply Plants in Gyeongnam Area
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Geosmin and 2-methyl isoborneol (2-MIB) levels in tap water and source water were estimated by comparingalgal species and populations for about one year from January to December 2013. The detected concentrationsof geosmin ranged from the method detection limit (MDL) to 274.0 (±17.0) ng/L. The highest levelof geosmin was found in the source water of Jinyang-ho lake during the first week of August. The highest levelof 2-MIB was observed in the source water of Changam water intake station in September, in the range ofMDL to 386.0 (±46.0) ng/L. Myeongdong and Shindosi water supply plants in Kimhae and Yangsan had goodperformance with as much as 100% removal efficiencies of odorous substances achieved in September, whenodorous substances usually reach the highest level during the year. Chilsu water supply plant was found torequire additional care to remove odorous substances because it had a similar level of 2-MIB with that of secondarydrinking water regulations. Jinju water supply plant, which did not have activated carbon filtration andozonation facilities, showed a geosmin level of 40.0 (±11.7) ng/L, higher than that of secondary drinking waterregulations. Cyanobacteria accounted for 47.9%, 48.3%, and 93.4% in Chilsu, Changam, and Mulgeum plantswhen 2-MIB concentrations were between 56.0 and 386.0 ng/L in September. Standing stocks of the dominantMicrocystis aeruginosa were also found different depending on the sampling sites: Chilsu, Changam, andMulgeum showed 18,000, 6,400, and 4,150 cells/mL, respectively. Further studies will be needed to betterunderstand the mechanisms of 2-MIB microbial production because it is still not be clear if the dominance ofMicrocystis aeruginosa leads to the highest level of 2-MIB directly.
Abstract
Geosmin and 2-methyl isoborneol (2-MIB) levels in tap water and source water were estimated by comparingalgal species and populations for about one year from January to December 2013. The detected concentrationsof geosmin ranged from the method detection limit (MDL) to 274.0 (±17.0) ng/L. The highest levelof geosmin was found in the source water of Jinyang-ho lake during the first week of August. The highest levelof 2-MIB was observed in the source water of Changam water intake station in September, in the range ofMDL to 386.0 (±46.0) ng/L. Myeongdong and Shindosi water supply plants in Kimhae and Yangsan had goodperformance with as much as 100% removal efficiencies of odorous substances achieved in September, whenodorous substances usually reach the highest level during the year. Chilsu water supply plant was found torequire additional care to remove odorous substances because it had a similar level of 2-MIB with that of secondarydrinking water regulations. Jinju water supply plant, which did not have activated carbon filtration andozonation facilities, showed a geosmin level of 40.0 (±11.7) ng/L, higher than that of secondary drinking waterregulations. Cyanobacteria accounted for 47.9%, 48.3%, and 93.4% in Chilsu, Changam, and Mulgeum plantswhen 2-MIB concentrations were between 56.0 and 386.0 ng/L in September. Standing stocks of the dominantMicrocystis aeruginosa were also found different depending on the sampling sites: Chilsu, Changam, andMulgeum showed 18,000, 6,400, and 4,150 cells/mL, respectively. Further studies will be needed to betterunderstand the mechanisms of 2-MIB microbial production because it is still not be clear if the dominance ofMicrocystis aeruginosa leads to the highest level of 2-MIB directly.
참고문헌 (21)
- 홍성균, "MBC 9시 뉴스에 보도된 “수도원 수돗물 악취녹조가 원인”에 대한 설명자료, 환경부 상하수도정책관실 수도정책과 보도설명자료", ~ (2011)
- Mallevialle, J, "Identification and treatment of tastes and odors in drinking water", AWWA Reasearch Foundation, pp.347~ (1987)
- 배병욱, "상수원수 내 조류 이취미에 관한 문헌고찰", 11, pp.57~72 (2007), The Institute of Environmental Studies(Daejeon University)
- Ho, L., "The effect of water quality and NOM character on the ozonation of MIB and geosmin", Water Science and Technology, 49(9), pp.249~255 (2004)
- AWWA, "Water quality and treatment" (1999), AWWA
- Whelton, A. J, "Relationship between intensity, concentration and temperature for drinking water odorants", Water Res, 38, pp.1604~1614 (2004)
- Watson, S. B., "Cyanobacyerial and eukaryotic algal odour compounds : signals or by-products? A review of their biological activity", Phycologia, 42, pp.332~350 (2003)
- 이화자, "수돗물의 냄새 유발물질 분석 및 처리", 박사, 환경공학, pp.2007
- 이가람, "유해 남조류의 성장 및 이취미 생산 특성 연구", 석사, 환경과학과, pp.2014
- 황석태, "2012년 상수도 통계 발표, 환경부 상수도 정책관실 수도정책과 보도자료, 2013. 12. 23", ~ (2013)
- 정진섭, "낙동강 주요 상수원 조류경보제 시범적용, 환경부 물환경정책국 수질관리과 보도자료, 2012. 2. 14", ~ (2012)
- 환경부, "수질오염공정시험기준, 환경부고시 제 2012-99호, 2012.6.11", ~ (2012)
- 환경부, "먹는물 수질감시항목 운영지침, 2013.12", ~ (2013)
- 이정호, "세포체적과 세포수에 의한 식물성플랑크톤의현존량 산정 비교", Korean J. Limnol, 31(3), pp.211~218 (1998)
- Blevins, W.T, "Comparative physiology of geosmin production by Streptomyces halstedii and Anabaena sp", Wat. Sci. Tech, 31(11), pp.127~133 (1995)
- 기후변화에 따른 담수호 수생태계 변화 조사 및 보전에 관한 연구(III), "유경아", 국립환경과학원 물환경연구부 유역생태연구팀, ~, pp.NIER-RP2012-284 (2012)
- 금강수계 따른이취미물질 생성현황 및 관리방안 연구, "양상용", 국립환경과학원 금강물환경연구소, ~, pp.NEIR NO. NIER-RP 2012-314 (2008)
- 김정아, "낙동강원수 중 이취물질과 방선균 및 조류의상관관계 연구", 부산광역시 상수도사업본부 수질연구소상수도연구원보 제13집, 13, pp.202~213 (2013)
- 유경아, "북한강 수계에서 이취미를 유발하는 남조류(Anabaena spiroides)의 증식 특성", 생태와 환경, 46(1), pp.135~144 (2013), 한국하천호수학회[DOI]
- 김진근, "팔당호의 조류 발생 특성", 대한환경공학회지, 31(5), pp.325~331 (2009), 대한환경공학회
- Rosen, B, "Accumulation and release of geosmin during the growth phases of anabaena circinalis", Water Scienceand Technology, 25, pp.185~190 (1992)
