Hazardous substance data, indicators and assessment
Second HELCOM BalticBOOST workshop
- n HOLAS II hazardous substance assessment
13-14 September 2016 Lena Avellan HELCOM Project Manager
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and assessment Second HELCOM BalticBOOST workshop on HOLAS II - - PowerPoint PPT Presentation
Hazardous substance data, indicators and assessment Second HELCOM BalticBOOST workshop on HOLAS II hazardous substance assessment 13-14 September 2016 Lena Avellan HELCOM Project Manager BalticBOOST HZ WS 9/13/2016 2-2016 1 HOLAS II
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(HELCOM MONAS 2012)
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Etc
Step 2 Step 1
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Core indictors GES boundary Clarifying comment Source Hexabromocyclo- dodecane (HBCDD) 167 µg/kg ww normalized to 5% lipid and adjusted to TL 4.5 EQS biota secondary
poisoning
Secondary GES boundary: sediment Polybrominated biphenyl ethers (PBDE) 0.0085 µg/kg ww fish liver and muscle normalized to 5% lipid and adjusted to TL 4 EQS biota human
health 1
Secondary boundary: sediment Perfluorooctane sulphonate (PFOS) 9.1 µg/kg ww fish muscle Normalized to 26% dw and adjusted to TL 4. Potential use of conversion factor between liver and muscle EQS biota human
health 1
Secondary GES boundary: 1.3 10-4 μg/l EQS water (AA) 1
[1] 2008/105/EC
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Core indicators GES boundary Clarifying comment Source Study reservation in place on GES boundary Metals Cd Coastal assessment unit 0.2 μg/l EQS water (AA)1 Secondary GES boundary: 2.3 mg/kg dw sediment QS Secondary GES boundary: 960 μg/kg dw blue mussel BAC Offshore assessment unit 50 μg/kg ww fish muscle 1000 μg/kg ww mussels EC 1881/2006 Poland Sweden (use of values for fish
muscle under Descriptor 8)
Denmark Pb Coastal assessment unit 1.3 μg/l EQS water (AA)1 Secondary GES boundary 120 mg/kg dw sediment QS 1300 μg/kg dw blue mussel BAC 26 μg/kg ww fish liver BAC5 Offshore assessment unit 300 μg/kg ww fish muscle 1500 μg/kg ww mussels EC 1881/2006 Poland Sweden (use of values for fish
muscle under Descriptor 8)
Denmark Hg 20 μg/kg ww fish muscle Normalized to 26% dw and adjusted to TL 4 EQS biota secondary
poisoning 1
[1] EU 2005. Substance Data Sheet Cadmium [2] EU 2011. Substance Data Sheet Lead
[3] OSPAR 2010. Background Document on CEMP assessment criteria for the QSR 2010 (proxy BACs derived at MON in 2007)
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Core indicator GES boundary Clarifying comment Source Study reservation Polyaromatic hydrocarbons (PAH) and their metabolites benzo(a)pyren e 5 μg/kg ww crustaceans and molluscs EQS biota human
health 1
Metabolite: 1- hydroxypyrene 483 ng/g fish bile Davies & Vethaak, 2012 Denmark Secondary GES boundary: Fluoranthene 30 μg/kg ww crustaceans and molluscs EQS biota human
health 1
2000 ug/kg dw sediment normalized to 5% TOC QS Denmark Secondary GES boundary: Anthracene 24 ug/kg dw sediment normalized to 5% TOC QS
[1] EU 2011. Substance Data Sheet Fluoranthene. [2] EU 2011. Substance Data Sheet Anthracene.
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Core indicator GES boundary Clarifying comment Source Study reser- vation Polychlorina ted biphenyls (PCB) and dioxins and furans Dioxin and dioxin-like PCBs 0.0065 TEQ/kg ww fish liver and muscle, crustaceans or molluscs normalized to 5% lipid and adjusted to TL 4 EQS biota
human health 1
Secondary GES boundary: CB-118 24 µg/kg lw fish liver and muscle: EACpassive5 Denmark Non-dioxin like PCBs sum of congeners (28, 52, 101, 138, 153, 180) 75 µg/kg ww fish muscle EC 1881/2006 Denmark
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Core indicator GES boundary Clarifying comment Source Study reser- vation TBT and imposex TBT 1.6 µg /kg dw sediment normalized to 5% TOC QS Denmark Secondary GES boundary: 0.2 ng/l water EQS water (AA)1 Secondary GES boundary: 12 µg/kg dw mussel EAC Denmark Imposex Peringia ulvae: 0.1 VDSI Nucella lapillus: 2.0 VDSI Neptunea antiqua: 2.0 VDSI Hinia reticulata: 0.3 VDSI Buccinum undatum: 0.3 VDSI Littorina littorea: <0.3 ISI HELCOM 2016 OSPAR EcoQO Denmark
[1] HELCOM 2016. Draft core indicator report on TBT and imposex [2] OSPAR 2008. Document 379. CEMP Assessment Manual Co-ordinated Environmental Monitoring Programme Assessment Manual for contaminants in sediment and biota [3] HELCOM 2016. Draft core indicator report on TBT and imposex [4] OSPAR 2010. EcoQO on imposex in dogwhelks and other selected gastropods. QUALITY STATUS REPORT 2010
Evaluation of the OSPAR system of EcoQOs for the North Sea, http://qsr2010.ospar.org/media/assessments/p00406_supplements/p00406_suppl_6_imposex_dogwhelks.pdf
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Core indicator GES bounadry Clarifying comment Source Study reservation White-tailed eagle productivity Productivity: 0.97 nestlings Brood size: 1.71 nestlings Breeding success: 0.59 (59%) HELCOM 2016 Denmark
[1] HELCOM 2016. Draft core indicator report white-tailed eagle productivity
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Pre-core (PC) or candidate indicator (cand) Proposal for GES boundary Reproductive disorders: Malformed eelpout and amphipod embryos (PC) Monoporeia affinis proportion of malformed embryos < 3.8% proportion of females with >1 malformed embryo <22% Gammarids Proportion of females with >1 malformed embryo <20% Eelpout Malformed fry <2% Late dead fry <4% Early dead fry <5% Lysosomal membrane stability (LMS) (PC) Histochemical method Herring and eelpout (liver) 8 min (EAC) Perch and flounder (liver) 10 min (EAC) All other species studied (liver, digestive gland)10 min (EAC) Neutral Red retention test Mytilus spp. (haemocytes) 50 min (EAC) Diclofenac concentration (PC) QS biota <1 µg kg-1 ww Secondary: EQS water 0.01 µg L-1 (AA) Estrogenic-like chemicals and effects (PC) <0.18 ng/l ethinyl estradiol equivalents (EEQ) EROD activity (cand) activities below 0.1 nmol/mg*min in microsomal fraction and 10 nmol/mg*min for S9 liver fraction
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