Interim report of the HELCOM CORESET project

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116 GES boundaries and matrix Existing quantitative targets e.g. EACs, BACs and food safety standards Table 3.14. Existing quantitative targets for TBT. Source OSPAR Value and description EAC sediment 0.01 ug TBT/kg DW EAC water 0.1 ng TBT/L EAC mussel 12 ug TBT/kg DW BAC/BC sediment Zero for man-made compound BAC/BC water Zero for man-made compound BAC/BC mussel Zero for man-made compound LC/BC mussel EC 1 ug TBT/kg DW EQS water Draft EQS water Draft EQS biota 0.2 ng TBT/L (AA) 1.5 ng TBT/L (MAC) Unoffi cial EQS sediment 0.02 ug TBT/kg DW Unoffi cial EQS biota 230 ug TBT/kg WW (predators second poisoning) Food stuff directive Effect Range -Low ERL sediment Other 15.2 ug TBT/kg WW for seafood PNEC AA 0.2 ng/L; MAC 1.5 ng/L TBT / 1.0 ng/L TPhT WHO (uptake by food) 0.25 ug per kilo of human weight per day Recommended GES boundaries Water: 0.2 ng/L Sediment: 0.02 ug/kg Biota: 12 ug/kg DW (for mussels) Seafood: 15.2 ug/kg WW for seafood Preferred matrix Water – Optional. (low solubility in water, high level of attachment to particles) Sediments – Optional. (Could be a co-factor in decreasing biodiversity in areas with low biodiversity) Biota (mussels or gastropoda snails): Preferred. (mussels are sensitive to TBT). Fish (liver) can be used as alternative if molluscs are not present.
Biological effects assessment classes for ECOQO on imposex/intersex Table 3.15. Imposex assessment classes for N. lapillus and other selected gastropods Assessment class N. lapillus L. littorea N. reticulatus B. undatum N. antiqua Criterion A VDSI ISI VDSI PCI VDSI Level of imposex is close to zero
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Baltic Sea Environment Proceedings
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2 Helsinki Commission Katajanokanla
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4 4.16. Cumulative impact on benthi
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6 descriptions of the indicators. T
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8 The CORESET expert group on biodi
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10 fi sh stocks and change in diet,
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12 Figure 2.3. The prevalence of pr
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14 Seasonal changes in blubber thic
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16 Blubber thickness suggestions Bl
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18 Weaknesses/gaps Monitoring of th
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20 2.3. Population growth rate of m
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22 Annual adult survival 1 0,95 0,9
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24 Existing monitoring data Informa
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26 References Bäcklin, B. M. 2011.
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28 Reproduction in the Baltic eagle
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30 Breeding success The proportion
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32 of the real number of nestlings
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34 Gaps and weaknesses Minimum dete
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36 2.5. Abundance of wintering popu
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38 Table 2.10. Pressures affecting
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40 Refrences Skov et al. (2000) Bir
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42 termined by application of the 7
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44 Approach for defi ning GES All s
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46 Sampling It is suggested to incl
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48 2.7. Fish population abundance 2
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50 Coastal Fish - Community Abundan
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52 When a reference data set cannot
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54 well, but were not included in t
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56 Weighting For Nordic Costal mult
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58 12. Current monitoring Monitored
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60 Błeńska M., Osowiecki A., Kra
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62 10. Spatial considerations Fucus
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64 2.15. Trend in the arrival of ne
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Page 72 and 73: 70 Strengths and weaknesses of data
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Page 78 and 79: 76 In Denmark, the highest contamin
Page 80 and 81: 78 Status of a compound on internat
Page 82 and 83: 80 A temporal analysis (EU-RAR 2006
Page 84 and 85: 82 Pathways of PFOS to the Baltic e
Page 86 and 87: 84 In regions less affected by anth
Page 88 and 89: 86 3.4. Polychlorinated biphenyls a
Page 90 and 91: 88 actions related to the environme
Page 92 and 93: 90 The CORESET expert group decided
Page 94 and 95: 92 pheric deposition pattern (lowes
Page 96 and 97: 94 3.5. Polyaromatic hydrocarbons (
Page 98 and 99: 96 GES boundaries and matrix Existi
Page 100 and 101: 98 Quality Assurance of PAH metabol
Page 102 and 103: 100 Ariese F, Burgers I, Oudhoff K,
Page 104 and 105: 102 GES boundaries and matrices Exi
Page 106 and 107: 104 3.7. Cesium-137 Authors: Jürge
Page 108 and 109: 106 Figure 3.5. Average surface lev
Page 110 and 111: 108 Temporal trends in concentratio
Page 112 and 113: 110 Other important sources are glo
Page 114 and 115: 112 Conceptual model of the sources
Page 116 and 117: 114 3.8 Tributyltin (TBT) and the i
Page 120 and 121: 118 Monitoring the compound Status
Page 122 and 123: 120 Recommendation TBT measurements
Page 124 and 125: 122 3. Frogs have been shown to app
Page 126 and 127: 124 not fi sh (Köhler et al. 2002;
Page 128 and 129: 126 The use of different fi sh spec
Page 130 and 131: 128 Kirchin, M.A. Moore, M.N. Dean,
Page 132 and 133: 130 3.11. Fish Disease Index: Exter
Page 134 and 135: 132 Confounding factors The multifa
Page 136 and 137: 134 analyses ICES data from various
Page 138 and 139: 136 An EAC is the threshold beyond
Page 140 and 141: 138 3.12. Micronucleus test Authors
Page 142 and 143: 140 main nuclei were not counted as
Page 144 and 145: 142 ing national data sets. Note: t
Page 146 and 147: 144 Baršienė J. Rybakovas A. 2006
Page 148 and 149: 146 3.13 A. Reproductive disorders
Page 150 and 151: 148 dead larvae can be induced by s
Page 152 and 153: 150 Strand, J, Dahllöf, I. (2005).
Page 154 and 155: 152 of contaminants in sediments wi
Page 156 and 157: 154 Eriksson Wiklund, A-K., and Sun
Page 158 and 159: 156 4. Candidate indicators for bio
Page 160 and 161: 158 Zooplankton-phytoplankton bioma
Page 162 and 163: 160 4.2. By-catch of marine mammals
Page 164 and 165: 162 4.3. Impacts of anthropogenic u
Page 166 and 167: 164 4.4. Fatty-acid composition of
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166 7. Use of the indicator in prev
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168 10. Spatial considerations Balt
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170 4.10. Large fi sh individuals f
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172 11. Temporal considerations Sam
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178 A proposal for an approach to a
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180 Technical data Metadata This is
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182 F igure 4.1. Map showing the cu
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184 4.17. Biomass of copepods 1. Wo
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186 4.19. Zooplankton species diver
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188 indirectly impacted by eutrophi
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190 Notes for the GES boundary The
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192 Step 3: Prepare a list of speci
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194 4.22. Phytoplankton diversity 1
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196 4. Policy relevance Nonylphenol
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198 among different studies/measure
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200 4.27. EROD/CYP1A induction The
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202 5.1. Summary of all supplementa
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204 Table 5.1. (continues) Suppleme
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206 5.5. Biopollution level index 1
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208 NIS for aquaculture purposes. O
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210 Balanus improvisus Baltic Katte
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212 Figure 5.3. The scheme for asse
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214 5.6. Organochlorine compounds G
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216 EU Directive 2008/105/ EC Daugh
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218 Table 5.4. Monitoring of HCB, H
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