Potential human health risks from metals (Hg, Cd, and Pb) and polychlorinated biphenyls (PCBs) via seafood consumption: Estimation of target hazard quotients (THQs) and toxic equivalents (TEQs)
Edible marine species (fish, cephalopod molluscs, crustaceans) from the Adriatic Sea were analyzed for content in heavy metals (Hg, Cd and Pb) and polychlorinated biphenyls (PCBs). Health risks to human via dietary intake of seafood were assessed by the target hazard quotients (THQs) and the toxic e...
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description | Edible marine species (fish, cephalopod molluscs, crustaceans) from the Adriatic Sea were analyzed for content in heavy metals (Hg, Cd and Pb) and polychlorinated biphenyls (PCBs). Health risks to human via dietary intake of seafood were assessed by the target hazard quotients (THQs) and the toxic equivalent factors (TEFs). Mercury maximum concentrations corresponded to fish (0.07–1.56
μg
g
−1
w.w.), followed by cephalopod molluscs (0.10–0.55
μg
g
−1
w.w.), and crustaceans (0.27–0.33
μg
g
−1
w.w.). Cadmium levels in cephalopods (0.18–0.59
μg
g
−1
w.w.) were higher than those in fish (0.01–0.05
μg
g
−1
w.w.) and crustaceans (0.02–0.04
μg
g
−1
w.w.), while for Pb the concentrations were generally low (fish: ND–1.18
μg
g
−1
w.w., cephalopods: ND–0.17
μg
g
−1
w.w., crustaceans: ND–0.03
μg
g
−1
w.w.). For PCBs, concentrations in fish, cephalopods and crustaceans ranged between 141 and 3406
ng
g
−1
l.w., 190 and 542
ng
g
−1
l.w., and 202 and 429
ng
g
−1
l.w., respectively. Cd and Pb THQ values as well as estimates of PCB TEQ exposure indicated the absence of health risks through consumption of the various seafood. In contrast, mercury TEQs values due to consumption of certain fish species (albacore, rosefish and thornback ray) indicated that human health risk might be of concern. |
doi_str_mv | 10.1016/j.fct.2008.05.011 |
format | Article |
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μg
g
−1
w.w.), followed by cephalopod molluscs (0.10–0.55
μg
g
−1
w.w.), and crustaceans (0.27–0.33
μg
g
−1
w.w.). Cadmium levels in cephalopods (0.18–0.59
μg
g
−1
w.w.) were higher than those in fish (0.01–0.05
μg
g
−1
w.w.) and crustaceans (0.02–0.04
μg
g
−1
w.w.), while for Pb the concentrations were generally low (fish: ND–1.18
μg
g
−1
w.w., cephalopods: ND–0.17
μg
g
−1
w.w., crustaceans: ND–0.03
μg
g
−1
w.w.). For PCBs, concentrations in fish, cephalopods and crustaceans ranged between 141 and 3406
ng
g
−1
l.w., 190 and 542
ng
g
−1
l.w., and 202 and 429
ng
g
−1
l.w., respectively. Cd and Pb THQ values as well as estimates of PCB TEQ exposure indicated the absence of health risks through consumption of the various seafood. In contrast, mercury TEQs values due to consumption of certain fish species (albacore, rosefish and thornback ray) indicated that human health risk might be of concern.</description><identifier>ISSN: 0278-6915</identifier><identifier>EISSN: 1873-6351</identifier><identifier>DOI: 10.1016/j.fct.2008.05.011</identifier><identifier>PMID: 18584931</identifier><identifier>CODEN: FCTOD7</identifier><language>eng</language><publisher>Oxford: Elsevier Ltd</publisher><subject>Algorithms ; Animals ; Biological and medical sciences ; cadmium ; Cadmium - analysis ; Cadmium - toxicity ; Cephalopoda ; Chemical and industrial products toxicology. Toxic occupational diseases ; chemical composition ; Crustacea ; Eating ; Environmental Pollutants - analysis ; Environmental Pollutants - toxicity ; estimation ; fish ; Fishes ; food composition ; food contamination ; Health risks ; Heavy metals ; human health ; Humans ; lead ; Lead - analysis ; Lead - toxicity ; Medical sciences ; mercury ; Mercury - analysis ; Mercury - toxicity ; Metals and various inorganic compounds ; Metals, Heavy - analysis ; Metals, Heavy - toxicity ; Mollusca ; molluscs ; polychlorinated biphenyls ; Polychlorinated Biphenyls - analysis ; Polychlorinated Biphenyls - toxicity ; Quality Control ; risk assessment ; Seafood ; Seafood - analysis ; Seafood - toxicity ; seafoods ; species differences ; Spectrophotometry, Atomic ; TEQs ; THQs ; toxicity ; Toxicology</subject><ispartof>Food and chemical toxicology, 2008-08, Vol.46 (8), p.2782-2788</ispartof><rights>2008 Elsevier Ltd</rights><rights>2008 INIST-CNRS</rights><lds50>peer_reviewed</lds50><woscitedreferencessubscribed>false</woscitedreferencessubscribed><citedby>FETCH-LOGICAL-c550t-41227794741be1704e9fc054d0f6ef6bfcd3a04994d1bba84fc809b67fd811d3</citedby><cites>FETCH-LOGICAL-c550t-41227794741be1704e9fc054d0f6ef6bfcd3a04994d1bba84fc809b67fd811d3</cites></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><linktohtml>$$Uhttps://www.sciencedirect.com/science/article/pii/S0278691508002366$$EHTML$$P50$$Gelsevier$$H</linktohtml><link.rule.ids>314,776,780,3537,27901,27902,65306</link.rule.ids><backlink>$$Uhttp://pascal-francis.inist.fr/vibad/index.php?action=getRecordDetail&idt=20558293$$DView record in Pascal Francis$$Hfree_for_read</backlink><backlink>$$Uhttps://www.ncbi.nlm.nih.gov/pubmed/18584931$$D View this record in MEDLINE/PubMed$$Hfree_for_read</backlink></links><search><creatorcontrib>Storelli, M.M.</creatorcontrib><title>Potential human health risks from metals (Hg, Cd, and Pb) and polychlorinated biphenyls (PCBs) via seafood consumption: Estimation of target hazard quotients (THQs) and toxic equivalents (TEQs)</title><title>Food and chemical toxicology</title><addtitle>Food Chem Toxicol</addtitle><description>Edible marine species (fish, cephalopod molluscs, crustaceans) from the Adriatic Sea were analyzed for content in heavy metals (Hg, Cd and Pb) and polychlorinated biphenyls (PCBs). Health risks to human via dietary intake of seafood were assessed by the target hazard quotients (THQs) and the toxic equivalent factors (TEFs). Mercury maximum concentrations corresponded to fish (0.07–1.56
μg
g
−1
w.w.), followed by cephalopod molluscs (0.10–0.55
μg
g
−1
w.w.), and crustaceans (0.27–0.33
μg
g
−1
w.w.). Cadmium levels in cephalopods (0.18–0.59
μg
g
−1
w.w.) were higher than those in fish (0.01–0.05
μg
g
−1
w.w.) and crustaceans (0.02–0.04
μg
g
−1
w.w.), while for Pb the concentrations were generally low (fish: ND–1.18
μg
g
−1
w.w., cephalopods: ND–0.17
μg
g
−1
w.w., crustaceans: ND–0.03
μg
g
−1
w.w.). For PCBs, concentrations in fish, cephalopods and crustaceans ranged between 141 and 3406
ng
g
−1
l.w., 190 and 542
ng
g
−1
l.w., and 202 and 429
ng
g
−1
l.w., respectively. Cd and Pb THQ values as well as estimates of PCB TEQ exposure indicated the absence of health risks through consumption of the various seafood. In contrast, mercury TEQs values due to consumption of certain fish species (albacore, rosefish and thornback ray) indicated that human health risk might be of concern.</description><subject>Algorithms</subject><subject>Animals</subject><subject>Biological and medical sciences</subject><subject>cadmium</subject><subject>Cadmium - analysis</subject><subject>Cadmium - toxicity</subject><subject>Cephalopoda</subject><subject>Chemical and industrial products toxicology. Toxic occupational diseases</subject><subject>chemical composition</subject><subject>Crustacea</subject><subject>Eating</subject><subject>Environmental Pollutants - analysis</subject><subject>Environmental Pollutants - toxicity</subject><subject>estimation</subject><subject>fish</subject><subject>Fishes</subject><subject>food composition</subject><subject>food contamination</subject><subject>Health risks</subject><subject>Heavy metals</subject><subject>human health</subject><subject>Humans</subject><subject>lead</subject><subject>Lead - analysis</subject><subject>Lead - toxicity</subject><subject>Medical sciences</subject><subject>mercury</subject><subject>Mercury - analysis</subject><subject>Mercury - toxicity</subject><subject>Metals and various inorganic compounds</subject><subject>Metals, Heavy - analysis</subject><subject>Metals, Heavy - toxicity</subject><subject>Mollusca</subject><subject>molluscs</subject><subject>polychlorinated biphenyls</subject><subject>Polychlorinated Biphenyls - analysis</subject><subject>Polychlorinated Biphenyls - toxicity</subject><subject>Quality Control</subject><subject>risk assessment</subject><subject>Seafood</subject><subject>Seafood - analysis</subject><subject>Seafood - toxicity</subject><subject>seafoods</subject><subject>species differences</subject><subject>Spectrophotometry, Atomic</subject><subject>TEQs</subject><subject>THQs</subject><subject>toxicity</subject><subject>Toxicology</subject><issn>0278-6915</issn><issn>1873-6351</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2008</creationdate><recordtype>article</recordtype><sourceid>EIF</sourceid><recordid>eNp9kc2u0zAQhSME4pYLD8AGvAFxpZviSez8wAqqQpGuRBFlbTn-aVySuLWdivJ2vBkujWDHaizNN8dn5iTJU8BzwFC83s21CPMM42qO6RwD3EtmUJV5WuQU7icznJVVWtRAr5JH3u8wxiWUxcPkCipakTqHWfJrbYMaguEdaseeD6hVvAstcsZ_90g726NeBd559Gq1vUULeYv4ING6uflT97Y7ibazzgw8KIkas2_VcDrj68V7f4OOhiOvuLZWImEHP_b7YOzwBi19MD0_v5HVKHC3VQG1_Cd3Eh1GG0x0FVU2qy_-8lWwP4xA6jCaI--m5jI2HycPdPSnnkz1Otl8WG4Wq_Tu88dPi3d3qaAUh5RAlpVlTUoCjYISE1VrgSmRWBdKF40WMueY1DWR0DS8IlpUuG6KUssKQObXycuL7N7Zw6h8YL3xQnUdH5QdPctiIoTQLIJwAYWz3jul2d7FTd2JAWbn2NiOxdjYOTaGKYuxxZlnk_jY9Er-m5hyisCLCeBe8E47Pgjj_3IZprTK6jxyzy-c5pbxbUyRffuaYcgxUEpIdlZ6eyFUvNXRKMe8iLcWShqnoi1pzX-M_gZ-NsAQ</recordid><startdate>20080801</startdate><enddate>20080801</enddate><creator>Storelli, M.M.</creator><general>Elsevier Ltd</general><general>Elsevier Science</general><scope>FBQ</scope><scope>IQODW</scope><scope>CGR</scope><scope>CUY</scope><scope>CVF</scope><scope>ECM</scope><scope>EIF</scope><scope>NPM</scope><scope>AAYXX</scope><scope>CITATION</scope><scope>7T2</scope><scope>7TV</scope><scope>7U2</scope><scope>7U7</scope><scope>C1K</scope><scope>F1W</scope><scope>H95</scope><scope>H97</scope><scope>L.G</scope></search><sort><creationdate>20080801</creationdate><title>Potential human health risks from metals (Hg, Cd, and Pb) and polychlorinated biphenyls (PCBs) via seafood consumption: Estimation of target hazard quotients (THQs) and toxic equivalents (TEQs)</title><author>Storelli, M.M.</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c550t-41227794741be1704e9fc054d0f6ef6bfcd3a04994d1bba84fc809b67fd811d3</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2008</creationdate><topic>Algorithms</topic><topic>Animals</topic><topic>Biological and medical sciences</topic><topic>cadmium</topic><topic>Cadmium - analysis</topic><topic>Cadmium - toxicity</topic><topic>Cephalopoda</topic><topic>Chemical and industrial products toxicology. Toxic occupational diseases</topic><topic>chemical composition</topic><topic>Crustacea</topic><topic>Eating</topic><topic>Environmental Pollutants - analysis</topic><topic>Environmental Pollutants - toxicity</topic><topic>estimation</topic><topic>fish</topic><topic>Fishes</topic><topic>food composition</topic><topic>food contamination</topic><topic>Health risks</topic><topic>Heavy metals</topic><topic>human health</topic><topic>Humans</topic><topic>lead</topic><topic>Lead - analysis</topic><topic>Lead - toxicity</topic><topic>Medical sciences</topic><topic>mercury</topic><topic>Mercury - analysis</topic><topic>Mercury - toxicity</topic><topic>Metals and various inorganic compounds</topic><topic>Metals, Heavy - analysis</topic><topic>Metals, Heavy - toxicity</topic><topic>Mollusca</topic><topic>molluscs</topic><topic>polychlorinated biphenyls</topic><topic>Polychlorinated Biphenyls - analysis</topic><topic>Polychlorinated Biphenyls - toxicity</topic><topic>Quality Control</topic><topic>risk assessment</topic><topic>Seafood</topic><topic>Seafood - analysis</topic><topic>Seafood - toxicity</topic><topic>seafoods</topic><topic>species differences</topic><topic>Spectrophotometry, Atomic</topic><topic>TEQs</topic><topic>THQs</topic><topic>toxicity</topic><topic>Toxicology</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Storelli, M.M.</creatorcontrib><collection>AGRIS</collection><collection>Pascal-Francis</collection><collection>Medline</collection><collection>MEDLINE</collection><collection>MEDLINE (Ovid)</collection><collection>MEDLINE</collection><collection>MEDLINE</collection><collection>PubMed</collection><collection>CrossRef</collection><collection>Health and Safety Science Abstracts (Full archive)</collection><collection>Pollution Abstracts</collection><collection>Safety Science and Risk</collection><collection>Toxicology Abstracts</collection><collection>Environmental Sciences and Pollution Management</collection><collection>ASFA: Aquatic Sciences and Fisheries Abstracts</collection><collection>Aquatic Science & Fisheries Abstracts (ASFA) 1: Biological Sciences & Living Resources</collection><collection>Aquatic Science & Fisheries Abstracts (ASFA) 3: Aquatic Pollution & Environmental Quality</collection><collection>Aquatic Science & Fisheries Abstracts (ASFA) Professional</collection><jtitle>Food and chemical toxicology</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Storelli, M.M.</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Potential human health risks from metals (Hg, Cd, and Pb) and polychlorinated biphenyls (PCBs) via seafood consumption: Estimation of target hazard quotients (THQs) and toxic equivalents (TEQs)</atitle><jtitle>Food and chemical toxicology</jtitle><addtitle>Food Chem Toxicol</addtitle><date>2008-08-01</date><risdate>2008</risdate><volume>46</volume><issue>8</issue><spage>2782</spage><epage>2788</epage><pages>2782-2788</pages><issn>0278-6915</issn><eissn>1873-6351</eissn><coden>FCTOD7</coden><abstract>Edible marine species (fish, cephalopod molluscs, crustaceans) from the Adriatic Sea were analyzed for content in heavy metals (Hg, Cd and Pb) and polychlorinated biphenyls (PCBs). Health risks to human via dietary intake of seafood were assessed by the target hazard quotients (THQs) and the toxic equivalent factors (TEFs). Mercury maximum concentrations corresponded to fish (0.07–1.56
μg
g
−1
w.w.), followed by cephalopod molluscs (0.10–0.55
μg
g
−1
w.w.), and crustaceans (0.27–0.33
μg
g
−1
w.w.). Cadmium levels in cephalopods (0.18–0.59
μg
g
−1
w.w.) were higher than those in fish (0.01–0.05
μg
g
−1
w.w.) and crustaceans (0.02–0.04
μg
g
−1
w.w.), while for Pb the concentrations were generally low (fish: ND–1.18
μg
g
−1
w.w., cephalopods: ND–0.17
μg
g
−1
w.w., crustaceans: ND–0.03
μg
g
−1
w.w.). For PCBs, concentrations in fish, cephalopods and crustaceans ranged between 141 and 3406
ng
g
−1
l.w., 190 and 542
ng
g
−1
l.w., and 202 and 429
ng
g
−1
l.w., respectively. Cd and Pb THQ values as well as estimates of PCB TEQ exposure indicated the absence of health risks through consumption of the various seafood. In contrast, mercury TEQs values due to consumption of certain fish species (albacore, rosefish and thornback ray) indicated that human health risk might be of concern.</abstract><cop>Oxford</cop><cop>New York, NY</cop><pub>Elsevier Ltd</pub><pmid>18584931</pmid><doi>10.1016/j.fct.2008.05.011</doi><tpages>7</tpages></addata></record> |
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language | eng |
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source | MEDLINE; Elsevier ScienceDirect Journals |
subjects | Algorithms Animals Biological and medical sciences cadmium Cadmium - analysis Cadmium - toxicity Cephalopoda Chemical and industrial products toxicology. Toxic occupational diseases chemical composition Crustacea Eating Environmental Pollutants - analysis Environmental Pollutants - toxicity estimation fish Fishes food composition food contamination Health risks Heavy metals human health Humans lead Lead - analysis Lead - toxicity Medical sciences mercury Mercury - analysis Mercury - toxicity Metals and various inorganic compounds Metals, Heavy - analysis Metals, Heavy - toxicity Mollusca molluscs polychlorinated biphenyls Polychlorinated Biphenyls - analysis Polychlorinated Biphenyls - toxicity Quality Control risk assessment Seafood Seafood - analysis Seafood - toxicity seafoods species differences Spectrophotometry, Atomic TEQs THQs toxicity Toxicology |
title | Potential human health risks from metals (Hg, Cd, and Pb) and polychlorinated biphenyls (PCBs) via seafood consumption: Estimation of target hazard quotients (THQs) and toxic equivalents (TEQs) |
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