Input coastal fish to HOLAS II (see document sent out via mail last week)
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1 Input coastal fish to HOLAS II (see document sent out via mail last week)
2 Input for coastal fish was submitted 31/ to HELCOM First, indicator status was scored per monitoring area using the assessment protocol for coastal fish (baseline or trendbased approach) => yielding whether or not the status per monitoring area is GES or subges (see doc 3-4)
3 To match the BEAT-tool as developed within HOLAS II, indicator status was normalized (0-1; 0 = min value and 1 = max value; threshold value 0.6). Max value Min value 0.125
4 How this was done: Baseline assessment Key species and piscivores Cyprinids/mesopredators *If upper threshold was used, then obs value = 0.6+(1-ln(assessment value +1)/value at upper threshold), which was classified to the neareast low value of 0.125, 0.375, or This concerns the data series Finnish ICES SD 29 and Finnish ICES SD 31 in Finland, and Kvädöfjärden long time series in Sweden ** If lower threshold was used then obs value =0.6+(1-ln(assessment value+1))/lower threshold, which was classified to the neareast low value of 0.125, 0.375, or 0.875, this only concerns the data series Finnish ICES SD 30, Finland.
5 How this was done: Trend-based assessment
6 KEY SPECIES Define initial condition If, then the not decrease If not, then the increase Assess trend If Increasing, If no trend, If decreasing If decreasing, If no trend, If increasing Transform to semiquantiative scale in order to merge indicator results based on different data types of monitoring */0.125** */0.875** *=p<0.1, **p<0.01
7 PISCIVORES Define initial condition If, then the not decrease If not, then the increase Assess trend If Increasing, If no trend, If decreasing If decreasing, If no trend, If increasing Transform to semiquantiative scale in order to merge indicator results based on different data types of monitoring */0.125** */0.825** *=p<0.1, **p<0.01
8 CYPRINIDS/MESOPREDATORS Define initial condition Assess trend If, then the not change If too high, then the decrease If too low, then the increase This did not occur If Increasing, If no trend, If decreasing, If no trend, If increasing Transform to semiquantiative scale in order to merge indicator results based on different data types of monitoring 0.375*/0.125** */0.875** *=p<0.1, **p<0.01
9 Like this (see file sent out via mail last week for details) 36 Bothnian Bay Finnish Coastal waters Finnish ICES SD Bothnian Bay Swedish Coastal waters Kinnbäcksfjärden Råneå The Quark Finnish Coastal waters 0.75 Finnish ICES SD Finnish ICES SD The Quark Swedish Coastal waters Holmön Norrbyn Belts Danish Coastal waters Århus Bay Fiords of Eastern Jutland Odense Fiord Sejerø Bay Southern Little Belt and the archipelago The Great Belt The Sound Danish Coastal waters The sound Gulf of Riga Estonian Coastal waters Hiiumaa Gulf of Riga Latvian Coastal waters Daugagriva Western Gotland Basin Swedish Coastal waters Kvädöfjärden Vinö 0.375
10 Aggregation from monitoring area to assessment unit scale 4 Status value for each assessment unit was derived by averaging the status across monitoring areas within assessment units
11 Confidence in assessment ConfA (confidence in assessment): - 1 = fisheries independent monitoring; = fisheries dependent monitoring targeting focal species; - 0 = fisheries dependent monitoring not targeting focal species (i.e. cyprinids) ConfT (confidence in temporal coverage): - 1 = all years included during ; = one or two years missing between ; - 0 = more than two years missing between ConfS (confidence in spatial coverage): - 1 = full coverage/several monitoring areas per assessment unit given its size; = two monitoring areas per assessment unit; - 0 = one monitoring area per assessement unit ConfM (confidence in methodology) - 1 = methodological standards (monitoring guidelines) in place = NA - 0 = NA
12 Like this (see file sent out via mail last week for details) Cyprinids/mesopredators 40 Medel av VALUE_series Medel av C_TEMPORAL Medel av C_SPATIAL Medel av C_ACCURACY Medel av C_METHODOLOGY IND TEMP SPAT ACC MONIT Bothnian Sea Finnish Coastal waters NA Finnish ICES SD NA Bothnian Sea Swedish Coastal waters NA Forsmark NA 1 1 Gaviksfjärden NA 1 1 Långvindsfjärden NA Åland Sea Swedish Coastal waters NA Lagnö NA Archipelago Sea Coastal waters NA Finbo NA 1 1 Finnish ICES SD NA 0 1 Kumlinge NA 1 1 Key species flounder 73 Medel av VALUE_series Medel av C_TEMPORAL Medel av C_SPATIAL Medel av C_ACCURACY Medel av C_METHODOLOGY IND TEMP SPAT ACC MONIT Belts Danish Coastal waters NA Århus Bay NA Fiords of Eastern Jutland NA Odense Fiord NA Sejerø Bay NA Southern Little Belt and the archipelago NA The Great Belt NA The Sound Danish Coastal waters NA The sound NA 0.5 1
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