The effect of redox conditions and adaptation time on organic micropollutant removal during river bank filtration: A laboratory-scale column study

被引:57
作者
Bertelkamp, C. [1 ,2 ]
Verliefde, A. R. D. [2 ]
Schoutteten, K. [2 ]
Vanhaecke, L. [3 ]
Vanden Bussche, J. [3 ]
Singhal, N. [4 ]
van der Hoek, J. P. [1 ,5 ]
机构
[1] Delft Univ Technol, Fac Civil Engn & Geosci, Dept Water Management, POB 5048, NL-2600 GA Delft, Netherlands
[2] Univ Ghent, Fac Biosci Engn, Particle & Interfacial Technol Grp, Coupure Links 653, B-9000 Ghent, Belgium
[3] Univ Ghent, Fac Vet Med, Dept Vet Publ Hlth & Food Safety, Chem Anal Lab, Salisburylaan 133, B-9820 Merelbeke, Belgium
[4] Univ Auckland, Dept Civil & Environm Engn, Private Bag 92019, Auckland 1142, New Zealand
[5] Waternet, Strateg Ctr, Korte Ouderkerkerdijk 7, NL-1096 AC Amsterdam, Netherlands
关键词
River bank filtration; Redox; Adaptation; Organic micropollutants; Biodegradation; MANAGED AQUIFER RECHARGE; PHARMACEUTICALLY ACTIVE COMPOUNDS; PRIMARY SUBSTRATE COMPOSITION; MICROBIAL COMMUNITY; WATER; SOIL; DEGRADATION; CHEMICALS; BEHAVIOR; CARBON;
D O I
10.1016/j.scitotenv.2015.11.035
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
This study investigated the redox dependent removal and adaptive behaviour of a mixture of 15 organic micropollutants (OMPs) in laboratory-scale soil columns fed with river water. Three separate pilot systems were used consisting of: (1) two columns, (2) ten columns and (3) twenty two columns to create oxic, suboxic (partial nitrate removal) and anoxic (complete nitrate removal). The pilot set-up has some unique features-it can simulate fairly long residence times (e.g., 45 days using the 22 column system) and reduced conditions developed naturally within the system. Dimethoate, diuron, and metoprolol showed redox dependent removal behaviour with higher biodegradation rates in the oxic zone compared to the suboxic/anoxic zone. The redox dependent behaviour of these three OMPs could not be explained based on their physico-chemical properties (hydrophobicity, charge and molecular weight) or functional groups present in the molecular structure. OMPs that showed persistent behaviour in the oxic zone (atrazine, carbamazepine, hydrochlorothiazide and simazine) were also not removed under more reduced conditions. Adaptive behaviour was observed for five OMPs: dimethoate, chloridazon, lincomycin, sulfamethoxazole and phenazone. However, the adaptive behaviour could not be explained by the physico-chemical properties (hydrophobicity, charge and molecular weight) investigated in this study and only rough trends were observed with specific functional groups (e.g. ethers, sulphur, primary and secondary amines). Finally, the adaptive behaviour of OMPs was found to be an important factor that should be incorporated in predictive models for OMP removal during river bank filtration. (C) 2015 Elsevier B.V. All rights reserved.
引用
收藏
页码:309 / 318
页数:10
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