Searching for a compromise between ecological quality targets, and social and ecosystem costs for heavily modified water bodies (HMWBs): the Lambro-Seveso-Olona system case study

被引:6
作者
Azzellino, A. [1 ]
Antonelli, M. [1 ]
Canobbio, S. [2 ]
Cevirgen, S. [1 ]
Mezzanotte, V. [2 ]
Piana, A. [3 ]
Salvetti, R. [1 ]
机构
[1] Politecn Milan, DICA, Environm Engn Div, I-20133 Milan, Italy
[2] Univ Milano Bicocca, DISAT, I-20126 Milan, Italy
[3] ARPA Lombardia, I-20124 Milan, Italy
关键词
heavily modified water bodies; QUAL2K; restoration; SOURCE APPORTIONMENT; RIVER; REUSE; LOADS;
D O I
10.2166/wst.2013.277
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
The Lambro-Seveso-Olona (L-S-O) system derives from the human regulation of the natural hydrology of the territory around Milan city area. The average population density in the L-S-O area is among the highest in Italy and Europe. Industry is also highly developed in this basin: chemical, textile, paper, pulp and food industries being the most important ones. Although, at present, the L-S-O system no longer receives the untreated wastewaters of the Milan urban area, treated wastewaters constitute about half of the streamflow. Biotic communities in this river have a long history of poor quality status, having suffered great damage due to domestic and industrial discharges. Recently, new chemical quality standards for macropollutants have been set by the Italian legislation as support for the good ecological status according to the Water Framework Directive (WFD). This new index is very restrictive, and it makes it extremely challenging to achieve the water quality objectives for the L-S-O system. The aim of this study is to analyse through a modelling exercise the restoration possibilities of the L-S-O system, investigating both the source apportionment of the macropollutants, the discharge limits that should be set to achieve the good quality status and their corresponding cost.
引用
收藏
页码:681 / 688
页数:8
相关论文
共 17 条
[1]   Combined use of the EPA-Qual2E simulation model and factor analysis to assess the source apportionment of point and non point loads of nutrients to surface waters [J].
Azzellino, A. ;
Salvetti, R. ;
Vismara, R. ;
Bonomo, L. .
SCIENCE OF THE TOTAL ENVIRONMENT, 2006, 371 (1-3) :214-222
[2]   INTEGRATED CHEMICAL AND BIOLOGICAL EVALUATION OF THE QUALITY OF THE RIVER LAMBRO (ITALY) [J].
BATTEGAZZORE, M ;
RENOLDI, M .
WATER AIR AND SOIL POLLUTION, 1995, 83 (3-4) :375-390
[3]   What does 'good ecological potential' mean, within the European water framework directive? [J].
Borja, Angel ;
Elliott, Michael .
MARINE POLLUTION BULLETIN, 2007, 54 (10) :1559-1564
[4]   BIOCONCENTRATION OF TRACE-METALS IN RAINBOW-TROUT - A FIELD-STUDY [J].
CAMUSSO, M ;
VIGANO, L ;
BALESTRINI, R .
ECOTOXICOLOGY AND ENVIRONMENTAL SAFETY, 1995, 31 (02) :133-141
[5]  
Chapra S.C., 2008, QUAL2K: A Modeling Framework for Simulating River and Stream Water Quality
[6]   Comparsion of membrane options for water reuse and reclamation [J].
Côté, P ;
Masini, M ;
Mourato, D .
DESALINATION, 2004, 167 (1-3) :1-11
[7]  
Cottrell A., 2011, GNU REGRESSION ECONO
[8]  
COVIRI, 2008, COM VIG US RIS IDR R
[9]  
DECAROLIS J, 2004, P WEFTEC 2004 NEW OR
[10]   The validation of common European class boundaries for river benthic macroinvertebrates to facilitate the intercalibration process of the Water Framework Directive [J].
Erba, Stefania ;
Furse, Mike T. ;
Balestrini, Raffaella ;
Christodoulides, Andreas ;
Ofenboeck, Thomas ;
van de Bund, Wouter ;
Wasson, Jean-Gabriel ;
Buffagni, Andrea .
HYDROBIOLOGIA, 2009, 633 (01) :17-31