Interim report of the HELCOM CORESET project
Interim report of the HELCOM CORESET project
Interim report of the HELCOM CORESET project
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need to be revisited in light <strong>of</strong> progress <strong>of</strong> EQS development in <strong>the</strong> EU and experience gained in <strong>the</strong>ir environmental<br />
application.<br />
All <strong>the</strong> proposed core indicators are listed in <strong>the</strong> summary table below and <strong>the</strong> following sections will provide<br />
descriptions <strong>of</strong> <strong>the</strong> proposed core indicators, including background documentation. Each core indicator has<br />
been given a separate section, following <strong>the</strong> numbering <strong>of</strong> <strong>the</strong> summary table.<br />
Table 3.1. Proposed core indicators for hazardous substances and <strong>the</strong>ir effects.<br />
Proposed core indicators Parameters<br />
Polybrominated biphenyl e<strong>the</strong>rs Congeners 28, 47, 99, 100, 153,154.<br />
Hexabromocyclododacene Hexabromocyclododacene (HBCD)<br />
Perfl uorooctane sulphonate Perfl uorooctane sulphonate (PFOS)<br />
Polychlorinated biphenyls and dioxins and furans CB congeners 28, 52, 101, 118, 138, 153 and 180.<br />
WHO-TEQ <strong>of</strong> dioxins and furans and dioxin-like PCBs.<br />
Polyaromatic hydrocarbons and <strong>the</strong>ir metabolites The US EPA 16 PAHs in bivalves and sediment and<br />
selected metabolites in fi sh.<br />
Metals Cadmium (Cd), mercury (Hg) and lead (Pb)<br />
Radioactive substances Caesium-137<br />
Tributyltin compounds / imposex index Tributyltin and/or imposex index<br />
Pharmaceuticals Dicl<strong>of</strong>enac and 17-alpha-ethinylestradiol<br />
General stress indicator Lysosomal membrane stability<br />
General stress indicator for fi sh Fish disease index<br />
Genotoxicity indicator Micronucleus induction<br />
Reproductive disorders Malformed embryos <strong>of</strong> eelpout and amphipods<br />
3.1. Poly Brominated Diphenyl e<strong>the</strong>rs (PBDE)<br />
General information 11<br />
Author: Jaakko Mannio<br />
Acknowledged persons:<br />
Anders Bignert, Elin Boalt, Anna Brzozowska, Galina<br />
Garnaga, Michael Haarich, Jenny Hedman, Ulrike<br />
Kamman, Thomas Lang, Martin M. Larsen, Kari<br />
Lehtonen, Rita Poikane, Rolf Schneider, Doris Schiedek,<br />
Jakob Strand, Joanna Szlinder-Richert, Tamara Zalewska<br />
General properties (e.g. herbicide, lipophilic, bioaccumulating, persistence, volatile)<br />
The polybrominated diphenyl e<strong>the</strong>rs (polyBDE) are diphenyl e<strong>the</strong>rs with degrees <strong>of</strong> bromination varying<br />
from 2 to 10. Among <strong>the</strong>se polyBDEs which are mainly used as fl ame retardants, three are available commercially:<br />
“pentaBDE commercial product”, “octaBDE commercial product” and “decaBDE commercial<br />
product”. However, <strong>the</strong>se products are all a mixtures <strong>of</strong> diphenyl e<strong>the</strong>rs as shown in <strong>the</strong> table hereunder.<br />
Therefore, to differentiate “pentaBDE commercial product” and “octaBDE commercial product” from<br />
“pentaBDE substance” and “octaBDE substance”, respectively, <strong>the</strong>se commercial products will be referred<br />
to as “c-pentaBDE” and “c-octaBDE” in <strong>the</strong> present fact sheet.<br />
All polyBDE’s are hydrophobic or very hydrophobic substances, are very likely to adsorb on particulate matter<br />
and not likely to volatilize from water phase. PBDEs have <strong>the</strong> potential to photodegrade in <strong>the</strong> environment.<br />
11 Following mostly <strong>the</strong> EU/CIRCA WFD /WGE draft dossier 22 Dec 2010