Three hundred ways to assess Europe's surface waters: An almost complete overview of biological methods to implement the Water Framework Directive

被引:795
作者
Birk, Sebastian [1 ]
Bonne, Wendy [2 ]
Borja, Angel [3 ]
Brucet, Sandra [2 ]
Courrat, Anne [4 ]
Poikane, Sandra [2 ]
Solimini, Angelo [5 ]
van de Bund, Wouter [2 ]
Zampoukas, Nikolaos [2 ]
Hering, Daniel [1 ]
机构
[1] Univ Duisburg Essen, Fac Biol, D-45141 Essen, Germany
[2] European Commiss, Joint Res Ctr, Inst Environm & Sustainabil, I-21027 Ispra, Italy
[3] AZTI Tecnalia, Div Marine Res, Pasaia 20110, Spain
[4] CEMAGREF UR EPBX, F-33612 Cestas, France
[5] Univ Roma La Sapienza, Dept Publ Hlth & Infect Dis, Rome, Italy
关键词
Bioassessment; Ecological status boundaries; Biological metric; Pressure-impact relationship; Taxonomic resolution; Sampling precision and representativeness; ECOLOGICAL STATUS; TAXONOMIC SUFFICIENCY; QUALITY; THRESHOLDS; INDICATORS; RECOMMENDATIONS; COMMUNITIES; ECOSYSTEMS; ESTUARINE; INTEGRITY;
D O I
10.1016/j.ecolind.2011.10.009
中图分类号
X176 [生物多样性保护];
学科分类号
090705 ;
摘要
According to the Water Framework Directive (WFD), the status of European surface waters is assessed using aquatic organism groups. Here we present an overview of 297 assessment methods, based on a questionnaire survey addressing authorities in all countries implementing the WFD. Twenty-eight countries reported on methods applied to rivers (30%), coastal waters (26%), lakes (25%) and transitional waters (19%). More than half of the methods are based on macroscopic plants (28%) or benthic invertebrates (26%); in addition, phytoplankton (21%), fish (15%) and phytobenthos (10%) were assessed. Countries of Central and Western Europe had developed almost all methods required for the WFD implementation. Two main sampling strategies were discernable: small-scale sampling of the taxonomically diverse groups of benthic invertebrates and phytobenthos that demand elaborate processing, versus large-scale sampling of vast, species-poor plant stands or the mobile fish fauna. About three-quarters of methods identified organisms to species-level while in particular phytoplankton-based methods used class-or phylum-level, or included no taxonomic information. Out of nine metric types distinguished, river methods used more sensitivity and trait metrics while for other water categories abundance metrics prevailed. Fish-based methods showed the highest number of metrics. Fifty-six percent of methods focussed on the detection of eutrophication and organic pollution, with shares decreasing from autotrophic to heterotrophic organism groups: phytoplankton > phytobenthos > macroscopic plants > benthic invertebrates > fish fauna. The order was almost reverse for hydrological or morphological deterioration: fish fauna and macroscopic plants > benthic invertebrates > phytoplankton > phytobenthos. These pressures were mainly assessed by methods applied to rivers and transitional waters. The pressure-impact relationship of about one-third of methods was not tested empirically with methods for transitional waters being the least validated. The strength of relationships differed significantly between organism groups and water categories. The correlation coefficients generally covered a broad range (<0.4 to >0.8), but on average with the pattern: phytoplankton > macroscopic plants > benthic invertebrates > phytobenthos and fish fauna. In terms of water categories the following order resulted: coastal waters > lakes > transitional waters > rivers. Status boundaries were mostly defined using statistical approaches. We advocate better reflection of the necessary sampling effort and precision, full validations of pressure-impact relationships and an implementation of more ecological components into classification. (C) 2011 Elsevier Ltd. All rights reserved.
引用
收藏
页码:31 / 41
页数:11
相关论文
共 78 条
[1]  
Adams S. M, 2002, BIOL INDICATORS AQUA
[2]  
[Anonymous], 2010, STATE OUTLOOK 2010 S, DOI DOI 10.2800/45773
[3]   A general framework for indicator design and use with application to the assessment of coastal water quality and marine protected area management [J].
Beliaeff, Benoit ;
Pelletier, Dominique .
OCEAN & COASTAL MANAGEMENT, 2011, 54 (01) :84-92
[4]   Comparing efficacy of different taxonomic resolutions and surrogates in detecting changes in soft bottom assemblages due to coastal defence structures [J].
Bertasi, Fabio ;
Colangelo, Marina Antonia ;
Colosio, Francesco ;
Gregorio, Gianni ;
Abbiati, Marco ;
Ceccherelli, Victor Ugo .
MARINE POLLUTION BULLETIN, 2009, 58 (05) :686-694
[5]  
Birk S., 2010, WISER methods database
[6]  
Birk Sebastian, 2005, Archiv fuer Hydrobiologie Supplement, V158, P171
[7]   A new procedure for comparing class boundaries of biological assessment methods: A case study from the Danube Basin [J].
Birk, Sebastian ;
Hering, Daniel .
ECOLOGICAL INDICATORS, 2009, 9 (03) :528-539
[8]   Developments in aquatic insect biomonitoring: A comparative analysis of recent approaches [J].
Bonada, N ;
Prat, N ;
Resh, VH ;
Statzner, B .
ANNUAL REVIEW OF ENTOMOLOGY, 2006, 51 :495-523
[9]   The European Water Framework Directive and the DPSIR, a methodological approach to assess the risk of failing to achieve good ecological status [J].
Borja, A ;
Galparsoro, I ;
Solaun, O ;
Muxika, I ;
Tello, EM ;
Uriarte, A ;
Valencia, V .
ESTUARINE COASTAL AND SHELF SCIENCE, 2006, 66 (1-2) :84-96
[10]   Overview of integrative tools and methods in assessing ecological integrity in estuarine and coastal systems worldwide [J].
Borja, Angel ;
Bricker, Suzanne B. ;
Dauer, Daniel M. ;
Demetriades, Nicolette T. ;
Ferreira, Joao G. ;
Forbes, Anthony T. ;
Hutchings, Pat ;
Jia, Xiaoping ;
Kenchington, Richard ;
Marques, Joao Carlos ;
Zhu, Changbo .
MARINE POLLUTION BULLETIN, 2008, 56 (09) :1519-1537