Sweden126. Swedish fish Index: Appelberg et al (2000) proposed a set <strong>of</strong> metrics based <strong>on</strong>standardised fish sampling, for assessing envir<strong>on</strong>mental disturbances in fishcommunities in Swedish lakes and streams. Reference values for the fish communitymetrics and scoring criteria in relati<strong>on</strong> to regi<strong>on</strong>al and local envir<strong>on</strong>ments wereestimated, using two comprehensive nati<strong>on</strong>al databases comprising fish communitydata from lakes and streams. In c<strong>on</strong>cordance with Minns et al. (1994), the databaseswere assumed to comprise both degraded and reference habitats.English127. IBI: Rahman et al. (2002) developed an index to assess ecological integrity inlowland rivers. The same IBI is also used in other countries as Finland, Italy,Lithuania, Netherlands, Spain and Switzerland.Other Fish Methods128. Czech Republic - Fish Stock assessment CEN/TC 230/WG 2/TG 4N (2001)Water analysis – Sampling <strong>of</strong> Fish with electricity. Revisi<strong>on</strong> <strong>of</strong> Pr EN 14011. 25.October 2001129. Denmark - Udvidet biologisk program. Skriver, J et al (1999)130. Finland - A fish based index for classificati<strong>on</strong> <strong>of</strong> the ecological status <strong>of</strong> riversis under development. In fish sampling <strong>of</strong> rivers, electr<strong>of</strong>ishing according to SFS –EN 14011 (Water analysis – sampling <strong>of</strong> fish with electricity is applied.131. France - Indice Poiss<strong>on</strong> en Riviere (FBI). Oberdorff, T et al (1992)132. Italy – Ichthyological Index (I.I. “Indice Ittico”). Lodi, E. Badino, G. (1993)Austria133. Several fish sampling <strong>methods</strong> are currently used in Austria. The main<strong>methods</strong> are electric fishing (in wadable streams or rivers), electric fishing from aboat, seining, gillnetting and l<strong>on</strong>g-lines (in large rivers, such as The Danube). Inwadable rivers, the number <strong>of</strong> electric fishing devices and the number <strong>of</strong> anodes aredependent <strong>on</strong> river width. Autumn is the preferred sampling seas<strong>on</strong> in wadable rivers.96
In n<strong>on</strong>-wadable or large rivers, the main sampling seas<strong>on</strong> is also in autumn, but alsoin the summer in the Danube.Belgium – Flanders134. The fish populati<strong>on</strong> surveys are standardised both for wadable and n<strong>on</strong>wadablerivers. The principal method <strong>of</strong> fish sampling is electric fishing, but other<strong>methods</strong> such as gillnets, seine netting or fyke nets are also used in large rivers, and insome specific water systems (e.g. in Polder drainage systems).135. In wadable rivers, the number <strong>of</strong> electric fishing devices and the number <strong>of</strong>anodes are dependent <strong>on</strong> river width, from 1 anode for river width smaller than 1.5 mto 4 anodes for rivers <strong>of</strong> 6-8 m wide. Electric fishing is performed in an upstreamdirecti<strong>on</strong>. At each stati<strong>on</strong> (sampled area = 100 m l<strong>on</strong>g), a maximum <strong>of</strong> 200 specimens<strong>of</strong> each species are individually weighed and measured). Captures by fyke nets, seinenetting and/or gill nets are sometimes used to complement the electric fishingcaptures, principally in standing waters (channels).Belgium – Wall<strong>on</strong>ia136. Despite the absence <strong>of</strong> a regular fish-m<strong>on</strong>itoring programme defined at theregi<strong>on</strong>al level, several instituti<strong>on</strong>s (Universities, public administrati<strong>on</strong> resp<strong>on</strong>sible <strong>of</strong>natural resource management) perform frequent fish sampling operati<strong>on</strong>s in Wall<strong>on</strong>ia.Electric fishing is used by all instituti<strong>on</strong>s, with relatively similar, but not standardised,sampling procedure. In additi<strong>on</strong>, fish capture data obtained with gill nets, seinenetting, fake nets or fish pass c<strong>on</strong>trol are also compiled in the regi<strong>on</strong>al fish database.137. In rivers, electric fishing is performed over a distance <strong>of</strong> 150-350 m,regardless <strong>of</strong> river width, with 1-3 passages depending <strong>on</strong> sampling objectives andinstituti<strong>on</strong>s. Stop nets are used as far as possible, but if the water flow is too high orthe river too wide, sampling areas are selected in such a way that natural barriers(small weirs or very shallow riffles) delimit the prospected z<strong>on</strong>es. The preferredsampling seas<strong>on</strong>s are summer and autumn.138. In n<strong>on</strong>-wadable rivers, electric fishing and horiz<strong>on</strong>tal bottom gill nettechniques are combined. Electric fishing is performed from a boat, in an upstream ordownstream directi<strong>on</strong> al<strong>on</strong>g both banks, by a staff <strong>of</strong> 4 pers<strong>on</strong>s including the anodeoperator. Both electric fishing and gill netting are usually performed during daylight,97
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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
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Lazaridou-Dimitriadou, M., C. Kouko
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Shannon, C.E. and W. Weaver, 1949.
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Annex I: Composition of the Geograp
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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
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- Page 76 and 77: countries also covers Non-EU Member
- Page 78 and 79: 49. The Danish Stream Fauna Index i
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- Page 82 and 83: Acidification Index, based on the s
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- 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
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- 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