Severity: Warning
Message: file_get_contents(https://...@gmail.com&api_key=61f08fa0b96a73de8c900d749fcb997acc09&a=1): Failed to open stream: HTTP request failed! HTTP/1.1 429 Too Many Requests
Filename: helpers/my_audit_helper.php
Line Number: 197
Backtrace:
File: /var/www/html/application/helpers/my_audit_helper.php
Line: 197
Function: file_get_contents
File: /var/www/html/application/helpers/my_audit_helper.php
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Function: simplexml_load_file_from_url
File: /var/www/html/application/helpers/my_audit_helper.php
Line: 3165
Function: getPubMedXML
File: /var/www/html/application/controllers/Detail.php
Line: 597
Function: pubMedSearch_Global
File: /var/www/html/application/controllers/Detail.php
Line: 511
Function: pubMedGetRelatedKeyword
File: /var/www/html/index.php
Line: 317
Function: require_once
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Background: Dietary intake, especially foods of animal-origin, is an important source of per- and polyfluoroalkyl substances (PFAS) exposure to the general population. However, the distribution of legacy and emerging PFAS in different food categories is unclear, as well as their potential health risk for children.
Objectives: To investigate dietary sources of PFAS and evaluate the risk for 7-year-old children in Laizhou Wan, a region with high PFAS exposure in Shandong, China.
Methods: We sampled participants from the Laizhou Wan Birth Cohort study. We administered a dietary questionnaire to the parents of 7-year-old children and measured PFAS compounds in the serum of the children (n = 154) and meat and seafood samples (n = 45). We calculated the Mann-Whitney U test to compare serum PFAS levels between children who frequently consumed a specific type of marine fish or shrimp/shellfish and those who did not. Children's dietary PFAS intake was calculated through multiplying food consumption and PFAS concentrations, and health risks were assessed by comparing the intake of PFAS with health-based guideline values.
Results: In seafood, perfluorooctanic acid (PFOA) (0.52 ng/g wet weight (ww)), perfluoro-6-methylheptanesulfonic acid (iso-PFOS) (0.02 ng/g ww), and 6:2 chlorinated polyfluoroethersulfonic acid (0.06 ng/g ww) had the highest median concentrations among 10 linear PFAS, 8 branched isomers of PFOA and perfluorooctanesulfonic acid (PFOS), and 3 alternatives, respectively. Particularly, PFOA levels (median, 87.80 ng/g) in (one type of marine fish), were approximately 10-100 times of those in other seafood species. Children who frequently consumed had higher serum PFAS levels, especially PFOA, than those who did not. Seafood intake accounted for more than 80% of the total estimated daily intake of PFAS. The dietary estimated weekly intake values of four PFAS (PFOA, PFOS, perfluorononanoic acid, and perfluorohexanesulfonic acid) for children (7.4 ng/kg of body weight (bw)/week) exceeded the tolerable weekly intake (4.4 ng/kg bw/week) as recommended by the European Food Safety Authority.
Conclusion: Seafood was widely contaminated by both legacy PFAS and their alternatives in Laizhou Wan area. Intake of seafood, especially , may contribute greatly to PFAS exposure in 7-year-old children. Avoiding intake of high PFAS polluted seafood may be an important strategy to protect local children. https://doi.org/10.1289/EHP15157.
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http://dx.doi.org/10.1289/EHP15157 | DOI Listing |