size <strong>of</strong> the net range between 250 to 750 µm. The models currently applied in variousnati<strong>on</strong>al watercourse m<strong>on</strong>itoring programmes differ in sampled area (0.01 to 0.12 m²)and mesh-size (100 to 500 µm).84. In deeper streams benthic macroinvertebrates are taken using grabs, dredges andartificial substrates. The applicati<strong>on</strong> <strong>of</strong> these devices is standardised in ISO 9391(1993) or EN ISO 9391 (1995). These are the same standards, as are the previous<strong>on</strong>es, as a result <strong>of</strong> adopti<strong>on</strong> by ISO and CEN. The difference in dates is caused by thedifferent dates <strong>of</strong> publicati<strong>on</strong> by the two organisati<strong>on</strong>s:85. In many European countries large rivers are m<strong>on</strong>itored by utilisati<strong>on</strong> <strong>of</strong>quantitative bottom samplers: Different types such as P<strong>on</strong>ar Grab, Van Veen Grab,Petersen Grab, Birge-Ekman Grab and core samplers are used. All devices sampledefined areas <strong>of</strong> the river bottom ranging from 100 to 500 cm².86. To obtain a qualitative sample <strong>of</strong> the river bed community, dredges representadequate tools in deeper watercourses. Dredges are particularly applied in severalcountries in the Danube catchment (Austria, Bulgaria, Hungary, Romania, Serbia-M<strong>on</strong>tenegro) using mesh-sizes <strong>of</strong> 225 and 500 µm.87. The use <strong>of</strong> artificial substrates allows comparability <strong>of</strong> different sites by providingsimilar habitats is not widely used for m<strong>on</strong>itoring purposes. In m<strong>on</strong>itoring programs<strong>on</strong>ly Moldova (Sapro<strong>biological</strong> assessment based <strong>on</strong> various metrics), Austria(Assessment <strong>of</strong> sapro<strong>biological</strong> quality <strong>of</strong> rivers) and France (I.B.G.N.) employ thesecol<strong>on</strong>isati<strong>on</strong> devices.88. Note that the ISO and CEN standards for sampling invertebrates are currentlyunder revisi<strong>on</strong>. This should make them more WFD compliant, but the timescale forpublicati<strong>on</strong> will inevitable be several years.Sampling frequency89. Sampling frequency in biom<strong>on</strong>itoring programmes using benthic invertebrates asindicators <strong>of</strong> watercourse quality varies from seas<strong>on</strong>al collecti<strong>on</strong>s to proceduresc<strong>on</strong>ducted every five years. Annual sampling is the most comm<strong>on</strong> interval applied inriver m<strong>on</strong>itoring. In particular, programs observing the sapro<strong>biological</strong> water qualityin Latvia, Moldova, Romania and Serbia-M<strong>on</strong>tenegro as well as the nati<strong>on</strong>al Italianm<strong>on</strong>itoring programme based <strong>on</strong> IBE take seas<strong>on</strong>al samples <strong>of</strong> macroinvertebrates.86
This inevitably influences the degree <strong>of</strong> uncertainty <strong>of</strong> the resulting ecologicalclassificati<strong>on</strong>s i.e. the likelihood <strong>of</strong> the banding allocated being accurate.MetricsLevel <strong>of</strong> tax<strong>on</strong>omical resoluti<strong>on</strong>90. The level <strong>of</strong> tax<strong>on</strong>omical resoluti<strong>on</strong> used in watercourse assessment <strong>methods</strong>based <strong>on</strong> macroinvertebrates differs.91. Nearly 60 percent <strong>of</strong> the bioassessment <strong>methods</strong> applied in Europe determine atleast selected orders <strong>of</strong> benthic invertebrates to species- or species groups-level. Thelatter intends to preserve some <strong>of</strong> the species-level informati<strong>on</strong> without the necessityto identify to species (Buffagni, 1997). The remaining approximately 40 percent <strong>of</strong><strong>methods</strong>, identify organisms to genus or family. Table 3 provides an overview <strong>of</strong>tax<strong>on</strong>omical resoluti<strong>on</strong> required in various quality assessment <strong>methods</strong> applied inEurope.Table 3. Tax<strong>on</strong>omical resoluti<strong>on</strong> required by various watercourse assessment <strong>methods</strong>applied in Europe.species-/species groups-levelgenus- and higher levelSaprobic Indices (applied in Austria, Bosnia-Herzegovina, Croatia, Czech Republic, Est<strong>on</strong>ia,Germany, Latvia, Lithuania, Moldova, Romania,Serbia-M<strong>on</strong>tenegro, Slovak Republic, Slovenia)Multimetric Indices (e.g. Austria, Germany andNetherlands)Functi<strong>on</strong>al Indices (PTI – Schöll and Haybach, 2001;LIFE Index – Extence et al., 1999)Acidificati<strong>on</strong> Indices (Germany - Braukmann and Biss,in print; Norway – Raddum, 1999)IOBS (AFNOR, 2002)PERLA (Kokeš et al., 2003)Swedish Benthic Fauna in Lake Littorals and RunningWater (SEPA, 2000)Acidificati<strong>on</strong> Index (Rutt et al., 1990)Belgian Biotic Index (De Pauw and Vanhooren, 1983)BMWP-ASPT Index (Armitage et al., 1983; Alba-Tercedor and Pujante, 2000) applied in Cyprus,Hungary, Spain, Portugal, Poland, United KingdomDanish Stream Fauna Index (Skriver et al., 2000)Extended Biotic Index (Ghetti, 1997)IGBN (AFNOR, 1992)Quality Rating Scheme (McGarrigle et al., 1992)Hellenic Evaluati<strong>on</strong> System (Lazaridou-Dimitriadou etal., 2004)92. Several <strong>methods</strong> demand the identificati<strong>on</strong> <strong>of</strong> genera <strong>on</strong>ly for particular groups <strong>of</strong>organisms (Table 4). The Italian as well as the Belgian index includes all genera <strong>of</strong>the orders Plecoptera, Ephemeroptera, Od<strong>on</strong>ata and the class Hirudinea am<strong>on</strong>gstothers. The identificati<strong>on</strong> <strong>of</strong> selected genera <strong>of</strong> st<strong>on</strong>eflies, gammarids and chir<strong>on</strong>omidsis required by the Danish and Irish schemes primarily mayflies to genera in the latter.In additi<strong>on</strong>, the DSFI comprises indicators <strong>of</strong> the orders megaloptera and coleoptera,and the genus Ancylus. The Irish Quality Rating Scheme c<strong>on</strong>siders individuals <strong>of</strong> a87
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Institute for Environment and Susta
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CONTENTSBackground and purpose of t
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Background and purpose of the docum
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States and candidate countries. Inf
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classification, each of these being
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BIOLOGICAL QUALITY ELEMENT: PHYTOPL
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indicators, species lists, frequenc
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53. The identification and enumerat
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64. In general, this technique is t
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RIVER BIOLOGICAL QUALITY ELEMENT: F
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84. The development of specific sta
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practice guides for identification
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100. The information received from
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Evaluation of the suitability of cu
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group should update its primary fin
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ReferencesAFNOR (Association Franç
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EN ISO 8689-2 Water quality - Biolo
- Page 35 and 36: Lazaridou-Dimitriadou, M., C. Kouko
- Page 37 and 38: Shannon, C.E. and W. Weaver, 1949.
- Page 39: Annex I: Composition of the Geograp
- Page 43 and 44: Annex III: River biological assessm
- Page 45 and 46: Annex IV: Analysis of lake biologic
- Page 47 and 48: Number of sampling stations10080%60
- Page 49 and 50: IT 90% acetone spectrophotometricPT
- Page 51 and 52: 10. The sampling depth and volume s
- Page 53 and 54: PTESFIIE5667-2/98 Romanianstandardi
- Page 55 and 56: Sampling stations%1008060402001 2-1
- Page 57 and 58: MACROPHYTES16. The aquatic Macrophy
- Page 59 and 60: Plants sampled per GIG1008060%40Eme
- Page 61 and 62: NO qualitativ method species number
- Page 63 and 64: indicators, species lists, frequenc
- Page 65 and 66: 26. The sampling frequency is varia
- Page 67: CEN/TC 230/WG 2/ TG 4 N28, 2 nd wor
- Page 70 and 71: programs are based only on the diat
- Page 72 and 73: 21. Some countries like France, Est
- Page 74 and 75: Table 1. European methods for monit
- Page 76 and 77: countries also covers Non-EU Member
- Page 78 and 79: 49. The Danish Stream Fauna Index i
- Page 80 and 81: Hungary58. Since 2002 a modificatio
- Page 82 and 83: Acidification Index, based on the s
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- Page 90 and 91: Table 5. Common abundance classific
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- Page 94 and 95: Austria120. MuLFA: Ecological Integ
- Page 96 and 97: Sweden126. Swedish fish Index: Appe
- Page 98 and 99: ut comparisons have been made with
- Page 100 and 101: seasons for sampling are summer and
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- Page 104 and 105: Consultation open to ECOSTAT &inter
- Page 106 and 107: Table 1. List of European standards
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- Page 110 and 111: development of typologySweden Yes,
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- Page 118 and 119: • Phytoplankton: Yes; Clorophyll
- Page 120 and 121: • Macroalgae: No• Benthic inver
- Page 122 and 123: • Macrophytes: No• Macroalgae:
- Page 124: Mission of the JRCThe mission of th