光州市 上水原水의 HANs 生成能에 관한 硏究

다국어 초록 (Multilingual Abstract)

Raw water for water supply contains various improper constituents such as suspended solids, colloids, dissolved organic materials or microbes which may cause turbidity and colorization. The main reason of applying chlorination could lead to sterilize microbes existing in the drinking water treatment. But chlorination could lead to the formation of disinfection by-products(DBPs) by the reaction of free chlorine with humic substance in the water.
This study was conducted to evaluate Haloacetonitriles Formation Portential(HANFP) by the variations of pH, contaction time and chlorine dose about the raw water
The formation concentration of HANs was increased with increasing chlorine dose, contact time and was reduced with increasing pH. HANFP and UV254 Absorbance showed high correlation by the variation of coagulant dose.
After 24 hours of chlorination, HANFP of raw water correlated with levels of Chlorine dosage and Re-Cl.
We also treated raw water with coagulation-sedimentation using Poly Aluminum Chloride(PAC) process. The concentration of HANFP ranged from 14.835 to 18.361㎍/ℓ in Dongbok.
At pH 6.0 the hightest HANFP measured after chlorination treatment in each raw water were 15.726㎍/ℓ(Dongbok), 11.88㎍/ℓ (Chuam), 21.449㎍/ℓ(Hwangryong).
At 48hours of chlorination treatment in each raw water were 13.472㎍/ℓ (Dongbok), 12.273㎍/ℓ(Chuam), 15.627㎍/ℓ(Hwangryong).

목차 (Table of Contents)

• 목차 = ⅰ
• List of Figures = ⅲ
• List of Tables = ⅳ
• Abstract = ⅴ
• Ⅰ. 서론 = 1
• Ⅱ. 문헌조사 = 2
• 1. 소독부산물 전구물질 = 2
• 1) 전구물질의 특성 = 2
• 2) 전구물질의 측정 = 4
• 2. 소독부산물의 생성 = 5
• 1) 음용수의 소독 = 5
• 2) 염소 소독부산물의 생성 = 5
• 3) 염소 소독부산물의 분류 = 6
• 4) THM, 할로아세틱산, 크로랄하이드레이트의 생성기구와 영향인자 = 8
• 5) 할로아세토니트릴의 생성기구 = 8
• 3. 소독부산물 전구물질의 제거방법 = 9
• Ⅲ. 실험내용 및 방법 = 10
• 1. 상수원의 지리적 특성 및 수질분석항목 = 10
• 1) 상수원의 지리적 특성 = 10
• 2) 분석 항목 = 10
• 3) HANs의 분석방법 = 11
• 2. 실험방법 = 19
• 1) 원수의 염소주입에 의한 HANs생성 = 19
• 2) 응집-침전-염소처리에 의한 UV_(254)흡광도, pH 및 HANs생성량 = 20
• 3) 영향인자에 따른 HANs 생성 및 UV_(254)흡광도 = 20
• Ⅳ. 결과 및 고찰 = 22
• 1. 원수의 수질특성 = 22
• 2. 원수의 염소처리에 의한 HANs의 생성능 = 23
• 3. 응집-침전-염소처리에 의한 HANs 생성능 = 27
• 1) PAC 주입에 따른 HANS와 UV_(254)흡광도의 상관관계 = 27
• 2) HANs와 pH의 상관관계 = 29
• 4. 영향인자에 따른 HANs생성과 UV254흡광도 = 30
• 1) pH에 따른 HANs의 생성과 UV254흡광도 = 30
• 2) 염소처리 후 시간에 따른 HANs생성과 UV254흡광도 = 33
• Ⅴ. 결론 = 36
• References = 37