Hazardous substances in marine organisms in Europe's seas

Hazardous substances are polluting Europe's seas, posing risks to ecosystems and human health. Nine hazardous substances were assessed in mussels and oysters between 2010 and 2022. Exceedance of safe limits was observed for benzo[a]pyrene, lindane (y-HCH), and polychlorinated biphenyl (PCB). Available time trends show that regions with improving (decreasing) concentrations are more prevalent than deteriorating ones. Therefore, further actions are essential to meeting the targets outlined in both the Marine Strategy Framework Directive and the Zero Pollution Action Plan.

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Metadata
DPSIR State
Typology Descriptive indicator (Type A - What is happening to the environment and to humans?)
UN SDGs SDG14: Life below water
Topics Water, Pollution, Seas and coasts, Biodiversity, Environmental health impacts
Temporal coverage { "readOnly": true, "temporal": [ { "label": "2010", "value": "2010" }, { "label": "2011", "value": "2011" }, { "label": "2012", "value": "2012" }, { "label": "2013", "value": "2013" }, { "label": "2014", "value": "2014" }, { "label": "2015", "value": "2015" }, { "label": "2016", "value": "2016" }, { "label": "2017", "value": "2017" }, { "label": "2018", "value": "2018" }, { "label": "2019", "value": "2019" }, { "label": "2020", "value": "2020" }, { "label": "2021", "value": "2021" }, { "label": "2022", "value": "2022" } ] }
Geographic coverage { "readOnly": true, "geolocation": [ { "label": "Adriatic Sea", "value": "geo-3183462" }, { "label": "Baltic Sea", "value": "geo-2633321" }, { "label": "Bay of Biscay", "value": "geo-2960858" }, { "label": "Black Sea", "value": "geo-630673" }, { "label": "Celtic Sea", "value": "geo-2960856" }, { "label": "Central Mediterranean Sea", "value": "CMED" }, { "label": "Greater North Sea", "value": "NSEA" }, { "label": "Iberian Coast", "value": "IC" }, { "label": "Ionian Sea", "value": "geo-2463713" }, { "label": "Mediterranean Sea", "value": "geo-363196" }, { "label": "North-East Atlantic Ocean", "value": "MATL" }, { "label": "Western Mediterranean Sea", "value": "WMED" } ] }
Workflow
Content responsible Head of Group Trine Christiansen
Layout
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true, "readOnly": true, "required": true, "section": false, "spacing": "m", "styles": {} }, "677f7422-6da4-4c86-bca8-de732b7047b9": { "@type": "dividerBlock", "disableNewBlocks": true, "fixed": true, "hidden": true, "readOnly": true, "required": true, "section": false, "spacing": "m", "styles": {} }, "96c53816-483c-4dca-a8ee-5c6d1afd0a92": { "@layout": "d060487d-88fc-4f7b-8ea4-003f14e0fb0c", "@type": "group", "allowedBlocks": [ "slate" ], "as": "section", "block": "96c53816-483c-4dca-a8ee-5c6d1afd0a92", "data": { "blocks": { "02ba4a04-fcfe-4968-806f-1dac3119cfef": { "@type": "embed_content", "disableNewBlocks": true, "fixed": true, "instructions": { "content-type": "text/html", "data": "<p><br/></p>", "encoding": "utf8" }, "readOnlySettings": true, "required": true, "url": "../../../../resolveuid/69344de00fce4f36aacfa74c12fa249e" }, "036a5909-95e3-4487-9b57-bf4bcd53e5d9": { "@type": "slate", "plaintext": "Higher concentrations result in larger risk of adverse effects for mussels and other aquatic organisms. The dioxin-like PCBs are also toxic to humans. The European Food Safety Authority set a tolerable weekly intake of dioxins and dioxin-like PCBs for humans in 2018. PCBs are typically transferred through the consumption of contaminated food, particularly meat, fish, and dairy .", "value": [ { "children": [ { "text": "Higher concentrations result in larger risk of adverse effects for mussels and other aquatic organisms. The dioxin-like PCBs are also " }, { "children": [ { "text": "toxic to humans." } ], "type": "strong" }, { "text": " The European Food Safety Authority set a tolerable weekly intake of dioxins and dioxin-like PCBs for humans in 2018. PCBs are typically transferred through the consumption of contaminated food, particularly meat, fish, and dairy" }, { "children": [ { "text": " " } ], "data": { "footnote": "<?xml version=\"1.0\"?>\n<div class=\"csl-bib-body\" style=\"line-height: 1.35; \">\n <div class=\"csl-entry\">Chain (CONTAM), E. P. on C. in the F., Knutsen, H. K., Alexander, J., Barreg&#xE5;rd, L., Bignami, M., Br&#xFC;schweiler, B., Ceccatelli, S., Cottrill, B., Dinovi, M., Edler, L., Grasl-Kraupp, B., Hogstrand, C., Nebbia, C. S., Oswald, I. P., Petersen, A., Rose, M., Roudot, A.-C., Schwerdtle, T., Vleminckx, C. et al., 2018, 'Risk for animal and human health related to the presence of dioxins and dioxin-like PCBs in feed and food', <i>EFSA Journal</i> 16(11), pp. e05333 (https://onlinelibrary.wiley.com/doi/abs/10.2903/j.efsa.2018.5333) accessed August 15, 2022.</div>\n</div>\n", "footnoteTitle": "Chain (CONTAM), EFSA Panel on Contaminants in the Food, 2018, Risk for animal and human health related, EFSA Journal", "uid": "TRRi9", "zoteroId": "QMS7XLDE" }, "type": "zotero" }, { "text": ". " } ], "type": "p" } ] }, "7ccb1d2f-3f68-4ca4-8c55-bc7f52d113b1": { "@type": "group", "className": "figure-metadata", "data": { "blocks": { "1c583e54-0ef7-47af-b68a-60babec087a0": { "@type": "slate", "plaintext": "Figure 2. Concentrations of PCB118 relative to assessment criteria", "value": [ { "children": [ { "text": "Figure 2. Concentrations of PCB118 relative to assessment criteria" } ], "type": "h3-light" } ] } }, "blocks_layout": { "items": [ "1c583e54-0ef7-47af-b68a-60babec087a0" ] } }, "id": "figure-metadata-02ba4a04-fcfe-4968-806f-1dac3119cfef", "styles": {} }, "7db9230b-2901-4414-ac67-9ccd62ee63d9": { "@type": "slate", "plaintext": "Figure 2 shows details of assessments of PCB118 in bivalves, i.e. blue mussel (Mytilus edulis and Mytilius galloprovincialis) and oysters (almost always Crassostrea gigas), during 2010-2022, with BAC and EAC indicated. Boxplots show a large percentage \u2018high\u2019 classifications (red points) often exceeding the EAC. The Western Mediterranean, Greater North, Celtic and Baltic Seas had stations where concentrations of PCB118 in mussels were more than 10 times the EAC.", "value": [ { "children": [ { "text": "Figure 2 shows details of assessments of PCB118 in bivalves, i.e. blue mussel (Mytilus edulis and Mytilius galloprovincialis) and oysters (almost always Crassostrea gigas), during 2010-2022, with BAC and EAC indicated. Boxplots show a large percentage \u2018high\u2019 classifications (red points) often exceeding the EAC. The Western Mediterranean, Greater North, Celtic and Baltic Seas had stations where concentrations of PCB118 in mussels were more than 10 times the EAC. " } ], "type": "p" } ] }, "c8cbfc02-20f5-4e18-a545-47d64eee48e5": { "@type": "slate", "plaintext": "Figure 2 also displays time trends for MSFD regions with ample data for assessment. The Greater North and Celtic Seas had a significant decrease in concentrations during this period. The estimate of the decrease is 20-30% per decade. For the Bay of Biscay and Baltic Sea, time series contained measurements under the detection limit, hence trends were not significant. Data were not sufficient for trend analysis in remaining areas.", "value": [ { "children": [ { "text": "Figure 2 also displays time trends for MSFD regions with ample data for assessment. The Greater North and Celtic Seas had a significant decrease in concentrations during this period. The estimate of the decrease is 20-30% per decade. For the Bay of Biscay and Baltic Sea, time series contained measurements under the detection limit, hence trends were not significant. Data were not sufficient for trend analysis in remaining areas." } ], "type": "p" } ] }, "d3d49723-14e5-4663-b346-37ee3572f28d": { "@type": "slate", "fixed": true, "instructions": { "content-type": "text/html", "data": "<p><br/></p>", "encoding": "utf8" }, "plaintext": "", "readOnlySettings": true, "required": true, "value": [ { "children": [ { "text": "" } ], "type": "p" } ] }, "43df8fab-b278-4b0e-a62c-ce6b8e0a881e": { "@type": "dividerBlock", "section": false, "short": true, "disableNewBlocks": true, "fixed": true, "hidden": true, "readOnly": true, "required": true, "spacing": "m", "fitted": false } }, "blocks_layout": { "items": [ "7ccb1d2f-3f68-4ca4-8c55-bc7f52d113b1", "02ba4a04-fcfe-4968-806f-1dac3119cfef", "43df8fab-b278-4b0e-a62c-ce6b8e0a881e", "7db9230b-2901-4414-ac67-9ccd62ee63d9", "036a5909-95e3-4487-9b57-bf4bcd53e5d9", "c8cbfc02-20f5-4e18-a545-47d64eee48e5" ] } }, "disableInnerButtons": true, "disableNewBlocks": false, "fixed": true, "ignoreSpaces": true, "instructions": { "content-type": "text/html", "data": "<ol keys=\"9bbul,b1sa2,171og,1c1t5\" depth=\"0\"><li>Depending on the indicator context, this text can provide information at country level or, if this is not relevant, at some other level, e.g. sectoral, regional level.</li><li>This text interprets the data represented in the chart, rather than describing results, i.e. it provides explanations for some of the results.</li><li>The text related to progress at this level does not have to be comprehensive.</li><li>If there is no information that adds value to what is already visible there is no need to have any text.</li></ol>", "encoding": "utf8" }, "maxChars": "1000", "placeholder": "Disaggregate level assessment e.g. country, sectoral, regional level assessment", "readOnly": false, "readOnlySettings": true, "required": true, "title": "Disaggregate level assessment" }, "9fa48b35-f2b5-45ae-a01b-b13d996b9838": { "@layout": "1bc4379d-cddb-4120-84ad-5ab025533b12", "@type": "group", "allowedBlocks": [ "slate" ], "as": "section", "block": "9fa48b35-f2b5-45ae-a01b-b13d996b9838", "data": { "blocks": { "194aeb29-82bf-4f2e-9aa3-572ad6d3374e": { "@type": "slate", "plaintext": "In the marine environment, hazardous substances accumulate in fish and shellfish, which are a food source for marine life, wildlife and humans. These contaminants are toxic for marine biota. Consuming contaminated seafood may generate adverse effects on human health such as organ failure, neurological disorders and increased cancer risk .", "value": [ { "children": [ { "text": "In the marine environment, hazardous substances accumulate in fish and shellfish, which are a food source for marine life, wildlife and humans. These contaminants are toxic for marine biota. Consuming contaminated seafood may generate " }, { "children": [ { "text": "adverse effects" } ], "type": "strong" }, { "text": " on human health such as organ failure, neurological disorders and " }, { "children": [ { "text": "increased cancer risk" } ], "data": { "extra": [], "footnote": "Noman, M. A., Feng, W., Zhu, G., Hossain, M. B., Chen, Y., Zhang, H. and Sun, J., 2022, 'Bioaccumulation and potential human health risks of metals in commercially important fishes and shellfishes from Hangzhou Bay, China' accessed 31 March 2025", "label": "Noman, M. A., Feng, W., Zhu, G., Hossain, M. B., Chen, Y., Zhang, H. and Sun, J., 2022, 'Bioaccumulation and potential human health risks of metals in commercially important fishes and shellfishes from Hangzhou Bay, China' accessed 31 March 2025", "uid": "iq6Ja", "value": "Noman, M. A., Feng, W., Zhu, G., Hossain, M. B., Chen, Y., Zhang, H. and Sun, J., 2022, 'Bioaccumulation and potential human health risks of metals in commercially important fishes and shellfishes from Hangzhou Bay, China' accessed 31 March 2025" }, "type": "footnote" }, { "text": ". " } ], "type": "p" } ] }, "1a82b84b-8762-4c02-a538-a2aa4a709d5b": { "@type": "slate", "plaintext": " Time trends largely reveal no (discernible) or unknown trend. For discernible trends, decreasing concentrations were more frequent than increasing. Decreasing trends represent lower concentrations and improved status. Further actions to decrease concentrations of contaminants in \u201chigh\u201d and \u201cmoderate\u201d classes should be taken.", "value": [ { "children": [ { "text": "" }, { "children": [ { "text": "" }, { "children": [ { "text": "Time trends" } ], "type": "strong" }, { "text": "" } ], "data": { "url": "../../../../resolveuid/7502e3e944e145b9b00d3d59b745a17d" }, "type": "link" }, { "text": " largely reveal no (discernible) or unknown trend. For discernible trends, decreasing concentrations were more frequent than increasing. Decreasing trends represent lower concentrations and improved status. Further actions to decrease concentrations of contaminants in \u201chigh\u201d and \u201cmoderate\u201d classes should be taken." } ], "type": "p" } ] }, "291bff78-7ad6-4c3c-a786-f19295e77e97": { "@type": "slate", "plaintext": " Classifications of hazardous substances measured in mussels and oysters between 2010-2022 are summarised below (also Figure 1). Concentrations were classified by several classifications: lower limits were either Environmental Quality Standards (EQS) in biota or OSPAR Background Assessment Concentrations (BAC) . Upper limits for the 'low' and 'moderate' classes were OSPAR Environmental Assessment Criteria (EAC), EQS in biota, or Maximum\u00a0Permissible Concentrations (MPC) for humans.", "value": [ { "children": [ { "text": "" }, { "children": [ { "text": "Classifications" } ], "type": "strong" }, { "text": " of hazardous substances" }, { "children": [ { "text": " " } ], "data": { "footnote": "<?xml version=\"1.0\"?>\n<div class=\"csl-bib-body\" style=\"line-height: 1.35; \">\n <div class=\"csl-entry\">EEA, 2011, <i>Hazardous substances in Europe&#x2019;s fresh and marine waters: an overview.</i>, Publications Office of the European Union, Luxembourg.</div>\n</div>\n", "footnoteTitle": "EEA, 2011, Hazardous substances in Europe's fresh a, Luxembourg", "uid": "c83wv", "zoteroId": "L9KUE4NB" }, "type": "zotero" }, { "text": " measured in mussels and oysters between 2010-2022 are summarised below (also Figure 1). Concentrations were classified by several classifications: lower limits were either " }, { "children": [ { "text": "Environmental Quality Standards (EQS)" } ], "data": { "extra": [], "footnote": "<?xml version=\"1.0\"?>\n<div class=\"csl-bib-body\" style=\"line-height: 1.35; \">\n <div class=\"csl-entry\">EU, 2013, Directive 2013/39/EU of the European Parliament and of the Council of 12 August 2013 amending Directives 2000/60/EC and 2008/105/EC as regards priority substances in the field of water policy, OJ L 226, 24.8.2013, p. 1&#x2013;17.</div>\n</div>\n", "footnoteTitle": "EU, Directive 2013/39/EU of the European Parliament and of the Council of 12 August 2013 amending Directives 2000/60/EC and 2008/105/EC as regards priority substances in the field of water policy", "uid": "KpmNe", "zoteroId": "RMH4CA2E" }, "type": "zotero" }, { "text": " in biota or OSPAR Background Assessment Concentrations (BAC)" }, { "children": [ { "text": "" } ], "data": { "footnote": "<?xml version=\"1.0\"?>\n<div class=\"csl-bib-body\" style=\"line-height: 1.35; \">\n <div class=\"csl-entry\">Dietz et al_2021_A risk assessment of the effects of mercury on Baltic Sea, Greater North Sea.pdf, (https://www.sciencedirect.com/science/article/pii/S0160412020321334/pdfft?md5=e5c7edb323d4244cae244fd7f1a8e0d2&amp;pid=1-s2.0-S0160412020321334-main.pdf&amp;isDTMRedir=Y) accessed August 15, 2022.</div>\n</div>\n", "footnoteTitle": " Dietz et al_2021_A risk assessment of th", "uid": "dGAMK", "zoteroId": "IBWPXAP9" }, "type": "zotero" }, { "text": ". Upper limits for the 'low' and 'moderate' classes were OSPAR Environmental Assessment Criteria (EAC), EQS in biota, or Maximum\u00a0Permissible Concentrations (MPC)" }, { "children": [ { "text": "" } ], "data": { "footnote": "<?xml version=\"1.0\"?>\n<div class=\"csl-bib-body\" style=\"line-height: 1.35; \">\n <div class=\"csl-entry\">EC, 2006, Commission Regulation (EC) No 1881/2006 of 19 December 2006 setting maximum levels for certain contaminants in foodstuffs&#xA0; (Text with EEA relevance), OJ L.</div>\n</div>\n", "footnoteTitle": "EC, Commission Regulation (EC) No 1881/2006 of 19 December 2006 setting maximum levels for certain contaminants in foodstuffs (Text with EEA relevance)", "uid": "11Vv3", "zoteroId": "DRBU5BYW" }, "type": "zotero" }, { "text": " for humans." } ], "type": "p" } ] }, "4ba76497-027d-4ac7-9639-ecaddbf56cf5": { "@type": "slate", "plaintext": "While evidence suggests a stabilisation in concentrations, it is imperative to implement measures such as stringent regulatory enforcement and promote safe and sustainable alternatives, aimed at preventing the generation of hazardous chemicals and reducing emissions at their source. Reducing concentrations of these substances helps achieve the MSFD Good Environmental Status and the targets set in the Zero Pollution Action Plan .", "value": [ { "children": [ { "text": "While evidence suggests a " }, { "children": [ { "text": "stabilisation" } ], "type": "strong" }, { "text": " in concentrations, it is imperative to implement measures such as stringent regulatory enforcement and promote safe and sustainable alternatives, aimed at preventing the generation of hazardous chemicals and reducing emissions at their source. Reducing concentrations of these substances helps achieve the " }, { "children": [ { "text": "MSFD Good Environmental Status" } ], "data": { "url": "https://msfd.eu/knowseas/library/commissiondescriptordecision.pdf" }, "type": "link" }, { "text": " and the targets set in the " }, { "children": [ { "text": "Zero Pollution Action Plan" } ], "data": { "url": "https://environment.ec.europa.eu/strategy/zero-pollution-action-plan_en" }, "type": "link" }, { "text": "." } ], "type": "p" } ] }, "5b8bda33-874a-4318-9700-66852b054cd5": { "@type": "slate", "plaintext": "The North-East Atlantic (NEA) Ocean and Mediterranean Sea demonstrate moderate to low levels of hazardous substances, with some high concentrations (PCBs for both areas, lindane and benzo[a]pyrene in addition for the Mediterranean Sea). The Baltic Sea displays moderate levels for most contaminants and high concentrations for PCB and lindane.", "value": [ { "children": [ { "text": "The North-East Atlantic (NEA) Ocean and Mediterranean Sea demonstrate moderate to low levels of hazardous substances, with some high concentrations (PCBs for both areas, lindane and benzo[a]pyrene in addition for the Mediterranean Sea). The Baltic Sea displays moderate levels for most contaminants and high concentrations for PCB and lindane. " } ], "type": "p" } ] }, "a35ece54-6690-45c9-b025-8226dd728d55": { "@type": "group", "className": "figure-metadata", "data": { "blocks": { "f5948be4-22a3-480a-9b9d-8fec722f99ea": { "@type": "slate", "plaintext": "Figure 1. Hazardous substances in mussels and oysters in Europe's seas", "value": [ { "children": [ { "text": "Figure 1. Hazardous substances in mussels and oysters in Europe's seas" } ], "type": "h3-light" } ] } }, "blocks_layout": { "items": [ "f5948be4-22a3-480a-9b9d-8fec722f99ea" ] } }, "id": "figure-metadata-b0279dde-1ceb-4137-a7f1-5ab7b46a782c", "styles": {} }, "b0279dde-1ceb-4137-a7f1-5ab7b46a782c": { "@type": "embed_content", "disableNewBlocks": true, "fixed": true, "instructions": { "content-type": "text/html", "data": "<p>figure instructions goes here</p>", "encoding": "utf8" }, "readOnlySettings": true, "required": true, "url": "../../../../resolveuid/35645c0e4a4a4f1f98b9d492aa5da8cb" }, "b30f1639-63f3-4d91-b31d-7ce0e16efe9a": { "@type": "slate", "plaintext": "Assessment of one PCB (dioxin-like PCB118) showed mainly \u2018high\u2019 in all regions. A significant part of the concentrations was classified as \u2018moderate\u2019. PCBs continue to pose a threat to marine ecosystems (Figure 2). ", "value": [ { "children": [ { "text": "Assessment of one PCB (dioxin-like PCB118) showed mainly \u2018high\u2019 in all regions. A significant part of the concentrations was classified as \u2018moderate\u2019. PCBs continue to pose a " }, { "children": [ { "text": "threat to marine ecosystems" } ], "type": "strong" }, { "text": " (Figure 2)." }, { "children": [ { "text": "" } ], "type": "b" }, { "text": "" } ], "type": "p" } ] }, "deb7e84d-d2c8-4491-90fa-3dc65fe02143": { "@type": "slate", "fixed": true, "instructions": { "content-type": "text/html", "data": "<p><br/></p>", "encoding": "utf8" }, "plaintext": "", "readOnlySettings": true, "required": true, "value": [ { "children": [ { "text": "" } ], "type": "p" } ] }, "f58853df-49f8-4148-9a8a-ba6fa6131546": { "@type": "slate", "plaintext": "Overall, the NEA Ocean and Mediterranean Sea have relatively lower concentrations of certain hazardous substances compared to the Baltic Sea. Yet, the presence of high concentrations still indicates ongoing challenges. The Baltic Sea stands out with consistent moderate levels across various substances, suggesting a less favorable status compared to the NEA Ocean and Mediterranean Sea.", "value": [ { "children": [ { "text": "Overall, the NEA Ocean and Mediterranean Sea have relatively lower concentrations of certain hazardous substances compared to the Baltic Sea. Yet, the presence of high concentrations still indicates ongoing challenges. The Baltic Sea stands out with consistent moderate levels across various substances, suggesting a less favorable status compared to the NEA Ocean and Mediterranean Sea." } ], "type": "p" } ] }, "43df8fab-b278-4b0e-a62c-ce6b8e0a881d": { "@type": "dividerBlock", "section": false, "short": true, "disableNewBlocks": true, "fixed": true, "hidden": true, "readOnly": true, "required": true, "styles": {}, "spacing": "m", "fitted": false } }, "blocks_layout": { "items": [ "a35ece54-6690-45c9-b025-8226dd728d55", "b0279dde-1ceb-4137-a7f1-5ab7b46a782c", "43df8fab-b278-4b0e-a62c-ce6b8e0a881d", "194aeb29-82bf-4f2e-9aa3-572ad6d3374e", "4ba76497-027d-4ac7-9639-ecaddbf56cf5", "291bff78-7ad6-4c3c-a786-f19295e77e97", "5b8bda33-874a-4318-9700-66852b054cd5", "f58853df-49f8-4148-9a8a-ba6fa6131546", "1a82b84b-8762-4c02-a538-a2aa4a709d5b", "b30f1639-63f3-4d91-b31d-7ce0e16efe9a" ] } }, "disableInnerButtons": true, "disableNewBlocks": false, "fixed": true, "ignoreSpaces": true, "instructions": { "content-type": "text/html", "data": "<p><strong>Assessment text remains at</strong> <strong>the relevant</strong> <strong>aggregate level</strong> <strong>(i.e.</strong> <strong>global, EU, sectoral)</strong> <strong>and addresses the following: </strong></p><ol keys=\"dkvn8,e367c,f4lpb,9j981,7ai6k,3g3pd\" depth=\"0\"><li>Explains in one or two sentences on the environmental rationale of the indicator, i.e. why it matters to the environment that we see an increase/decrease in the value measured.</li><li>Explains in one or two sentences the associated policy objective, which can be either quantitative or directional. More information on the policy objective and related references will be included in the supporting information section. Where there is no policy objective associated with the indicator, i.e. where the indicator addresses an issue that is important for future policy formulation, this text should explain instead why this issue is important.</li><li>IF NECESSARY - Explains any mismatch between what the indicator tracks and what the policy objective/issue is.</li><li>Qualifies the historical trend (e.g. steady increase) and explains the key reasons (e.g. policies) behind it. If there is a quantitative target it explains if we are on track to meet it.</li><li>IF NECESSARY - Explains any recent changes to the trend and why.</li><li>IF NECESSARY - Describes what needs to happen to see adequate progress in future, for instance in order to remain on track to meet targets.</li></ol><p><strong>Please cite your work if</strong> <strong>necessary</strong> <strong>using the EEA citation style (i.e.</strong> <strong>EEA, 2020). A full reference list appears in the supporting information section.</strong></p>", "encoding": "utf8" }, "maxChars": "2000", "placeholder": "Aggregate level assessment e.g. progress at global, EU level..", "readOnlySettings": true, "required": true, "title": "Aggregate level assessment" }, "e9736b7c-4902-48aa-aecd-b706409a576d": { "@type": "dividerBlock", "disableNewBlocks": true, "fixed": true, "hidden": true, "readOnly": true, "required": true, "section": false, "spacing": "m", "styles": {} }, "ea13f90f-4d5d-4f85-9452-3485f03a963e": { "@layout": "794c9b24-5cd4-4b9f-a0cd-b796aadc86e8", "@type": "group", "allowedBlocks": [], "as": "section", "block": "ea13f90f-4d5d-4f85-9452-3485f03a963e", "data": { "blocks": { "12d8c532-f7ad-43fe-ada7-330b2d7a7a39": { "@type": "slate", "disableNewBlocks": true, "fixed": true, "instructions": { "content-type": "text/html", "data": "<p><br/></p>", "encoding": "utf8" }, "plaintext": "Published: date \u2012 25min read", "readOnly": true, "readOnlySettings": true, "required": true, "value": [ { "children": [ { "text": "" }, { "children": [ { "text": "Published: " }, { "children": [ { "text": "date" } ], "data": { "id": "effective", "widget": "datetime" }, "type": "mention" }, { "text": " \u2012 25min read" } ], "type": "sup" }, { "text": "" } ], "type": "p" } ] }, "1c31c956-5086-476a-8694-9936cfa6c240": { "@type": "description", "disableNewBlocks": true, "fixed": true, "instructions": { "content-type": "text/html", "data": "<p>The summary tells the reader about the indicator trend over the examined period and whether or not it helps to achieve the associated policy objective, which can be either quantitative or directional.</p><p>In the absence of a policy objective, it explains whether the trend is in the right or wrong direction in relation to the issue examined.</p><p>If there has been an important change over the most recent period of the time series, e.g. over the last year, this is indicated too.</p><p>Furthermore, if there is a quantitative target, it also indicates whether we are on track to meet it and if not what are the reasons preventing that, e.g. socio-economic drivers, implementation gap etc.</p>", "encoding": "utf8" }, "placeholder": "Summary", "plaintext": "Hazardous substances are polluting Europe's seas, posing risks to ecosystems and human health. Nine hazardous substances were assessed in mussels and oysters between 2010 and 2022. Exceedance of safe limits was observed for benzo[a]pyrene, lindane (y-HCH), and polychlorinated biphenyl (PCB). Available time trends show that regions with improving (decreasing) concentrations are more prevalent than deteriorating ones. Therefore, further actions are essential to meeting the targets outlined in both the Marine Strategy Framework Directive and the Zero Pollution Action Plan.", "readOnlySettings": true, "required": true, "value": [ { "children": [ { "text": "Hazardous substances are polluting Europe's seas, posing risks to ecosystems and human health. Nine hazardous substances were assessed in mussels and oysters between 2010 and 2022. Exceedance of safe limits was observed for benzo[a]pyrene, lindane (y-HCH), and polychlorinated biphenyl (PCB). Available time trends show that regions with improving (decreasing) concentrations are more prevalent than deteriorating ones. Therefore, further actions are essential to meeting the targets outlined in both the Marine Strategy Framework Directive and the Zero Pollution Action Plan." } ], "type": "p" } ] }, "3cccc2bb-471a-44c7-b006-5595c4713ff2": { "@type": "layoutSettings", "disableNewBlocks": true, "fixed": true, "layout_size": "narrow_view", "readOnly": true, "readOnlySettings": true, "required": true }, "ddde07aa-4e48-4475-94bd-e1a517d26eab": { "copyrightIcon": "ri-copyright-line", "styles": {}, "variation": "default", "@type": "title", "disableNewBlocks": true, "fixed": true, "hideContentType": true, "hideCreationDate": true, "hideDownloadButton": true, "hideModificationDate": true, "placeholder": "Indicator title", "readOnlySettings": true, "required": true } }, "blocks_layout": { "items": [ "ddde07aa-4e48-4475-94bd-e1a517d26eab", "1c31c956-5086-476a-8694-9936cfa6c240", "3cccc2bb-471a-44c7-b006-5595c4713ff2" ] } }, "disableInnerButtons": true, "disableNewBlocks": true, "fixed": true, "fixedLayout": true, "ignoreSpaces": true, "instructions": { "content-type": "text/html", "data": "<p>The summary tells the reader about the indicator trend over the examined period and whether or not it helps to achieve the associated policy objective, which can be either quantitative or directional.</p><p>In the absence of a policy objective, it explains whether the trend is in the right or wrong direction in relation to the issue examined.</p><p>If there has been an important change over the most recent period of the time series, e.g. over the last year, this is indicated too.</p><p>Furthermore, if there is a quantitative target, it also indicates whether we are on track to meet it and if not what are the reasons preventing that, e.g. socio-economic drivers, implementation gap etc.</p>", "encoding": "utf8" }, "maxChars": "500", "readOnlySettings": true, "required": true, "styles": { "style_name": "environment-theme-bg" }, "title": "Content header" } }
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Supporting information
Methodology [ { "children": [ { "text": "Concentrations of the nine hazardous substances were collected from two databases: ICES (" }, { "children": [ { "text": "www.ices.dk" } ], "data": { "url": "http://www.ices.dk" }, "type": "link" }, { "text": ") and EMODNET Chemistry (" }, { "children": [ { "text": "https://www.emodnet-chemistry.eu/" } ], "data": { "url": "https://www.emodnet-chemistry.eu/" }, "type": "link" }, { "text": "). The databases contain measurements for a large number of species, but to achieve a relatively homogenous dataset, only data from bivalves of the following species were used: " }, { "children": [ { "text": "Cerastoderma edule" } ], "type": "i" }, { "text": " (common cockle), " }, { "children": [ { "text": "Mya arenaria" } ], "type": "i" }, { "text": " (softshell clam), " }, { "children": [ { "text": "Ruditapes philippinarum" } ], "type": "i" }, { "text": " (Manila clam), " }, { "children": [ { "text": "Mytilus edulis" } ], "type": "i" }, { "text": " (blue mussel), " }, { "children": [ { "text": "M. galloprovincialis" } ], "type": "i" }, { "text": " (Mediterranean mussel), " }, { "children": [ { "text": "Crassostrea gigas" } ], "type": "i" }, { "text": " (Pacific oyster), " }, { "children": [ { "text": "Ostrea edulis" } ], "type": "i" }, { "text": " (native oyster) and " }, { "children": [ { "text": "Macoma balthica" } ], "type": "i" }, { "text": " (Baltic clam). This left us with approximately 300,000 measurements. Approximately 10% of the stations had data in both databases and needed database cleaning to avoid using the same measurement from both databases. Furthermore, only data from the late summer and autumn were used, as concentrations of mussels in the spring are affected by spawning. For status, the 90% percentile over the 10 year period 2010-2022 was used to classify concentrations in 'low', 'moderate', and 'high' classes using two threshold values per contaminant (some thresholds also differ between blue mussels and oysters). The lower of the two thresholds was mostly OSPAR's BAC criterion or EQS (for cadmium and mercury).\u00a0The higher threshold value was either the EQS from the WFD, OSPAR EAC, or Maximum Permissible Concentration (MPC) for seafood security. In order to calculate status, at least one year (Mediterranean) or three years (other areas) of data since 2010 were needed. For trends, dry-weight concentrations for metals and wet-weight concentrations for organic substances were used. Data before 2005 were excluded and trends were calculated for time series of 5-10 years that ended in 2015 or later. If the data series had no median concentrations under LOQ, we used linear regression; otherwise, a Bayesian model (with non-informative priors) implemented in " }, { "children": [ { "text": "JAGS" } ], "data": { "extra": [], "footnote": "Plummer, M.; Stukalov, A.; Denwood, M. Rjags: Bayesian Graphical Models Using MCMC, 2024. (https://cran.r-project.org/web/packages/rjags/index.html) accessed 09 January 2025", "label": "Plummer, M.; Stukalov, A.; Denwood, M. Rjags: Bayesian Graphical Models Using MCMC, 2024. (https://cran.r-project.org/web/packages/rjags/index.html) accessed 09 January 2025", "uid": "b__uD", "value": "Plummer, M.; Stukalov, A.; Denwood, M. Rjags: Bayesian Graphical Models Using MCMC, 2024. (https://cran.r-project.org/web/packages/rjags/index.html) accessed 09 January 2025" }, "type": "footnote" }, { "text": " was used." } ], "type": "p" }, { "children": [ { "text": "" } ], "type": "p" }, { "children": [ { "text": "" } ], "type": "p" } ]
Data sources and providers { "readOnly": true, "data": [ { "@id": "21dfeb21-79c0-442d-aa3a-f1f3ff63f75b", "title": "ICES DOME (Marine Environment)", "link": "https://www.ices.dk/data/data-portals/Pages/DOME.aspx", "organisation": "International Council for the Exploration of the Sea (ICES)" }, { "@id": "7632c08f-3bd6-4c7e-82a1-c0dcd0d021d2", "title": "EMODnet Chemistry", "link": "https://www.emodnet-chemistry.eu/", "organisation": "European Marine Observation and Data Network (EMODnet)" }, { "@id": "710c7386-328d-40a3-901a-0861d6628853", "title": "Regional seas around Europe - version 2, Oct. 2022", "link": "https://www.eea.europa.eu/en/datahub/datahubitem-view/d09a1d82-8e11-4448-85a5-e2613aeccf57?activeAccordion=1083843", "organisation": "European Environment Agency (EEA)" } ] }
Definition [ { "children": [ { "text": "The indicator is based on concentrations of nine hazardous substances measured in eight species of mussels and oysters. The nine substances are cadmium (Cd), mercury (Hg), lead (Pb), Copper (Cu), hexachlorobenzene (HCB), lindane (gamma-hexachlorocyclohexane, HCHG), DDT (using the breakdown product p,p'-DDE), benzo[a]pyrene (BAP) and 2,3',4,4',5-Pentachlorobiphenyl (PCB118). For each station, the 90% percentile over the 10 year period 2010-2022 was used to classify concentrations in \u2018low\u2019, \u2018moderate\u2019 and \u2018high\u2019 classes. These classifications are based on OSPAR's Background Assessment Concentrations (BAC) criteria, the Environmental Quality Standards (EQS) from the EU Water Framework Directive (WFD) and the Maximum Permissible Concentration (MPC) for food." } ], "type": "p" } ]
Unit of measure [ { "children": [ { "text": "Index and percentage (%)" } ], "type": "p" } ]
Policy / environmental relevance [ { "children": [ { "text": "The " }, { "type": "link", "data": { "url": "https://environment.ec.europa.eu/topics/marine-environment_en" }, "children": [ { "text": "MSFD website" } ] }, { "text": "" }, { "children": [ { "text": " " } ], "type": "sup" }, { "text": "states that \u2018human activities affect the marine environment through the release of chemical contaminants, which degrade the state of marine waters and can cause serious damage to its functioning\u2019. The indicator is based on bivalves, which live as water filterers and are very effective \u2018harvesters\u2019 of any contaminants found in the water. In our process of selecting contaminants, we wanted to have contaminants that have been recorded in as many parts of Europe as possible \u2014 as well as contaminants that span a range of sources and behave differently in the environment. For instance, mercury is very volatile, which makes the atmosphere (including rain) an important source. Many of the other contaminants are mostly found in the aquatic environment. Many of the contaminants \u2014 such as DDT, lindane \u2014 represent \u2018legacy\u2019 contaminants. These are now largely banned but still exist in the environment, including in ocean sediments. " } ], "type": "p" } ]
Frequency of dissemination 1
Accuracy and uncertainties [ { "children": [ { "text": "There is a large variation in coverage between regions and parameters \u2014 with especially low coverage in the Black Sea. It is important to use sensitive analytical measurements that have sufficiently quantification levels. Of the 182 species in the databases, there were 86 fish species, and species monitored vary between regions (e.g. there were 64 fish species in the Atlantic region, but only four fish species in the Mediterranean). Assessment of contaminants in fish from high trophic levels are important supplement to mussel data for identifying risks to human health. Possibly normalisation to lipid content or dry weight as described in " }, { "children": [ { "text": "the implementation strategy for the Water Framework Directive" } ], "data": { "extra": [], "footnote": "European Commission. Common Implementation Strategy for the Water Framework Directive (2000/60/EC). Guidance Document No. 32 on Biota Monitoring (the Implementation of EQSbiota) under the Water Framework Directive.; Technical Report; Publications Office: Luxembourg, 2014.", "label": "European Commission. Common Implementation Strategy for the Water Framework Directive (2000/60/EC). Guidance Document No. 32 on Biota Monitoring (the Implementation of EQSbiota) under the Water Framework Directive.; Technical Report; Publications Office: Luxembourg, 2014.", "uid": "28OK1", "value": "European Commission. Common Implementation Strategy for the Water Framework Directive (2000/60/EC). Guidance Document No. 32 on Biota Monitoring (the Implementation of EQSbiota) under the Water Framework Directive.; Technical Report; Publications Office: Luxembourg, 2014." }, "type": "footnote" }, { "text": " could be used to get an overview. " } ], "type": "p" }, { "type": "p", "children": [ { "text": "" } ] }, { "children": [ { "text": "Also, \u2018novel\u2019 contaminants such as per- and polyfluoroalkyl substances (PFAS) were not included in the indicator because there was no coverage in the Mediterranean and Black Sea regions. PFAS were analysed by only a limited number of countries of which PFOS was the most common PFAS reported. There was high variation in species, tissue and coverage of different PFAS analysed. A direct comparison of levels between regions is therefore challenging. Exceedances of the current EQS for PFOS was observed for mammals, birds and fish. The highest exceedances were observed for polar bears with 100 times exceedances of EQS. The current EQS for PFOS will probably be replaced by a proposed and much lower EQS for the sum of " }, { "children": [ { "text": "24 PFAS" } ], "data": { "extra": [], "footnote": "European Commission. European Commission - Have your say. European Commission - Have your say. https://eur-lex.europa.eu/legal-content/EN/TXT/?uri=CELEX:52022PC0540 Accessed 21 January 2025", "label": "European Commission. European Commission - Have your say. European Commission - Have your say. https://eur-lex.europa.eu/legal-content/EN/TXT/?uri=CELEX:52022PC0540 Accessed 21 January 2025", "uid": "yLzlt", "value": "European Commission. European Commission - Have your say. European Commission - Have your say. https://eur-lex.europa.eu/legal-content/EN/TXT/?uri=CELEX:52022PC0540 Accessed 21 January 2025" }, "type": "footnote" }, { "text": "" } ], "type": "p" } ]
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Short name hazardous-substances-in-marine-organisms
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Contents
Concentrations of PCB118 relative to assessment criteria

The figure shows concentrations of PCB118 relative to the assessment criteria BAC (Background Assessment Concentration) and EAC (Environmental Assessment Criteria as given by OSPAR). For instance, a point at '4x EAC' indicates a site where the observed concentration was four (4) times the EAC limit. The points have been spread horizontally to avoid too much overlap.

Hazardous substances in mussels and oysters in Europe's seas

The figure shows one map for each of the selected contaminants. Each of the small dots in the map represents a station (a location which is regularly monitored), coloured according to estimated concentration levels (low/moderate/high relative to environmental thresholds). The big pie diagrams show, for each region, the proportion of stations that have low/moderate/high concentration levels. The legend by each monitoring station shows whether the environmental status is improving (decreasing concentrations), deteriorating (increasing concentrations), shows no significant change (no trend) or no discernable trend (trend unknown).