Report on Harmonisation of freshwater biological methods

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Acidification Index, based on the sensitivity of the various taxa, is used to assess theeffects of acidification. The classification system is modified to cover acidification oforganic rivers. In eutrophication studies, different indices such as the Modified TrentIndex, BMWP, ASTP, Shannon-Weaver are used.69. Knowledge on Norwegian river macroinvertebrates is based on nationalmonitoring programs on acidification and liming (22 rivers including only non-limedsites) and various surveys related to effects of local pollution and river regulations(approx. 900 sites).Poland70. The BMWP system provides a score for each macroinvertebrate family that isprimarily dependant on its sensitivity to organic pollution. In use in the UnitedKingdom since the late 1970s, this method is intended to be applied in Poland,operating with a modified list of indicator taxa. It is recently elaborated and will soonbe utilised within a pilot project. To verify the results obtained by calculating theBMWP score, a diversity index expressed as the ratio of number of families tomacroinvertebrate fauna abundance is determined.Portugal71. For WFD-compliant monitoring the BMWP' will be used which is an adaptation ofthe British Biological Monitoring Working Party (BMWP) score system. Themodifications include the addition of new families, changes in some scores anddivision of scores into five classes, representing various degrees of organic pollution.Romania72. Monitoring of aquatic biota throughout Romania is conducted four times per yearwithin the framework of the National Water Monitoring System, which started in1978. In the past, biological quality assessment was based on the Relative LoadMethod (Knöpp, 1955). Now, biological quality assessment of running waters is basedon the determination of the Saprobic Index according to Pantle and Buck (1955).Since the beginning of 2004 the index scores have been classified in a five-bandscheme following the recommendations of Knoben et al. (1999).82
73. In preparation of WFD implementation a national stream typology has beendeveloped. In addition, a multimetric assessment method was completed, whichdetermines the biological water quality based on the effects of organic pollution, toxicsubstances and morphological degradation.Spain74. Within the Spanish project GUADALMED a method to assess the ecologicalstatus of streams and rivers in the Spanish Mediterranean area has been developed(ECOSTRIMED). The main objective of ECOSTRIMED is to provide an integratedquality assessment system for fluvial ecosystems. It includes the riparian habitat andthe biological quality of the water as the main parameters. Designed as a RapidBioassessment Protocol (RBP) it is performed directly in the field with a shortsampling time schedule.75. The ECOSTRIMED index is calculated by combining the values of two differentquality indices: 1) a biological index based on macroinvertebrates (FBILL orIBMWP), 2) a Riparian Habitat Quality Index (QBR). In accordance with therequirements of the WFD the result is presented in one of five classes of ecologicalstatus.Sweden76. The Time Series as a component of the Swedish method Benthic Fauna in LakeLittorals and Running Water uses four selected indicator metrics of macroinvertebratediversity and distribution: Shannon’s Diversity Index, ASPT Index, Danish StreamFauna Index and Acidity Index according to Hendikson and Medin. This approachleads to an assessment of watercourses (riffle areas), resulting in one of five conditionclasses for each metric. The ratio between observed index value and expectedreference value is used to indicate the extent to which bottom fauna conditions deviatefrom an undisturbed (natural) state.Switzerland77. Switzerland uses the component Benthos biology of the Methods for Investigationand Assessment of running waters to evaluate biological watercourse quality. Themethod‘s objectives are to gain information on the occurrence of commonmacroinvertebrate taxa and to appraise and assess impacts on its composition.83
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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
Page 31 and 32: ReferencesAFNOR (Association Franç
Page 33 and 34: 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 84 and 85: Identification is predominantly to
Page 86 and 87: size of the net range between 250 t
Page 88 and 89: water bug genus (Aphelocheirus) and
Page 90 and 91: Table 5. Common abundance classific
Page 92 and 93: 108. Process Assessment focuses on
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
Page 102 and 103: 102
Page 104 and 105: Consultation open to ECOSTAT &inter
Page 106 and 107: Table 1. List of European standards
Page 108 and 109: 108
Page 110 and 111: development of typologySweden Yes,
Page 112 and 113: one or other option depends on the
Page 114 and 115: 114
Page 116 and 117: • An integrated holistic evaluati
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
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Report on Harmonisation of freshwater biological methods

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