Activated soil filters (bio filters) for the elimination of xenobiotics (micro-pollutants) from storm- and waste waters

被引:35
作者
Bester, Kai [1 ,2 ]
Schaefer, Daniel [2 ]
机构
[1] Aalborg Univ, Dept Biotechnol Chem & Environm Engn, DK-9000 Aalborg, Denmark
[2] Univ Duisburg Essen, Inst Environm Analyt Chem, D-45141 Essen, Germany
关键词
Bio filter; Storm water; Hydrophilic xenobiotic compounds; Triclosan; Flame retardants; SEWAGE-TREATMENT PLANTS; PERSONAL CARE PRODUCTS; FLAME RETARDANTS; SURFACE WATERS; CONSTRUCTED WETLANDS; MUSK FRAGRANCES; REMOVAL; PHARMACEUTICALS; BIOFILTRATION; TRICLOSAN;
D O I
10.1016/j.watres.2009.03.026
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
A technical scale (0.12 m(3)) activated soil filter (bio filter) has been used to eliminate diverse xenobiotics (organic micro-pollutants) such as organophosphate flame retardants, and -plasticisers, musk fragrances, DEHP, benzothiazoles and triclosan from water. Model experiments to treat combined sewer overflow, storm water and a post treatment of waste water were performed in controlled laboratory experiments. The indicator compounds were typical for waste water. Diverse chemical compound groups and a wide spectrum from the lipophilic (pK(ow) = 5.9) to the hydrophilic (pK(ow) = 2.6) were included. The system consisted of a layer with high organic content (with vegetation to prevent clogging), a sand filter and a gravel drainage layer. The organic layer was spiked with activated sludge to enhance biomass and biodegradation potential. Usually the elimination rates varied from 64% to 99%, with only one compound reaching as little as 17%. For a technical suitability assessment it was calculated how long these filters would be stable in eliminating organic compounds from water. The estimated operating times for such systems was found to be about 100 years for a stack height of 2 m a year in regard to most compounds in this study (C) 2009 Elsevier Ltd. All rights reserved.
引用
收藏
页码:2639 / 2646
页数:8
相关论文
共 38 条
[1]   Triclosan, a commonly used bactericide found in human milk and in the aquatic environment in Sweden [J].
Adolfsson-Erici, M ;
Pettersson, M ;
Parkkonen, J ;
Sturve, J .
CHEMOSPHERE, 2002, 46 (9-10) :1485-1489
[2]   Packed bed dynamics during microbial treatment of wastewater: Modelling and simulation [J].
Agarwal, G. K. ;
Ghoshal, A. K. .
BIORESOURCE TECHNOLOGY, 2008, 99 (09) :3765-3773
[3]   Elimination of organophosphate ester flame retardants and plasticizers in drinking water purification [J].
Andresen, J ;
Bester, K .
WATER RESEARCH, 2006, 40 (03) :621-629
[4]   Organophosphorus flame retardants and plasticisers in surface waters [J].
Andresen, JA ;
Grundmann, A ;
Bester, K .
SCIENCE OF THE TOTAL ENVIRONMENT, 2004, 332 (1-3) :155-166
[5]   Occurrence of some organic UV filters in wastewater, in surface waters, and in fish from Swiss lakes [J].
Balmer, ME ;
Buser, HR ;
Müller, MD ;
Poiger, T .
ENVIRONMENTAL SCIENCE & TECHNOLOGY, 2005, 39 (04) :953-962
[6]  
BESTER B, 2008, WATER AIR SOIL POLL, V8, P407
[7]   Retention characteristics and balance assessment for two polycyclic musk fragrances (HHCB and AHTN) in a typical German sewage treatment plant [J].
Bester, K .
CHEMOSPHERE, 2004, 57 (08) :863-870
[8]   Triclosan in a sewage treatment process - balances and monitoring data [J].
Bester, K .
WATER RESEARCH, 2003, 37 (16) :3891-3896
[9]   Fate of triclosan and triclosan-methyl in sewage treatment plants and surface waters [J].
Bester, K .
ARCHIVES OF ENVIRONMENTAL CONTAMINATION AND TOXICOLOGY, 2005, 49 (01) :9-17
[10]  
Bester K., 2007, Personal Care Compounds in the Environment, Pathways, Fate, and Methods of Determination