| Fish, freshwater (tilapia, catfish, trout) | 100% | µg/kg f.w. | Perch, Finnish rivers and coastal sites (n = 48), fresh weight; detection frequency | PDF p.9, Table 5, PFNA row, Perch Detection Frequency column | PFASs in Finnish Rivers and Fish and the Loading of PFASs to the Baltic Sea |
| Fish, freshwater (tilapia, catfish, trout) | 0.23 | µg/kg f.w. | Perch, Finnish rivers and coastal sites (n = 48), fresh weight; mean | PDF p.9, Table 5, PFNA row, Perch Mean column | PFASs in Finnish Rivers and Fish and the Loading of PFASs to the Baltic Sea |
| Fish, freshwater (tilapia, catfish, trout) | 1.1 | µg/kg f.w. | Perch, Finnish rivers and coastal sites (n = 48), fresh weight; maximum | PDF p.9, Table 5, PFNA row, Perch Max column | PFASs in Finnish Rivers and Fish and the Loading of PFASs to the Baltic Sea |
| Seafood | 0.07 ± 0.01 | ng/g | Fish cake, untreated control, Korea; mean ± SD | PDF p.5, Table 2, PFNA row, Control column | Reduction of perfluorinated compound content in fish cake and swimming crab by different cooking methods |
| Fish, freshwater (tilapia, catfish, trout) | 0.16 (0.06-0.29) | µg/kg | Coregonus wartmanni fillets, Switzerland 2022-2024 (N = 20); average (min-max) | PDF p.5, Table 1, PFNA row, Coregonus wartmanni Av (min-max) column | Determination of per- and polyfluoroalkyl substances (PFAS) in six different fish species from Swiss lakes |
| Fish, freshwater (tilapia, catfish, trout) | 50% | µg/kg | Coregonus wartmanni fillets, Switzerland 2022-2024 (N = 20); frequency of positives above LOQ | PDF p.5, Table 1, PFNA row, Coregonus wartmanni F (%) column | Determination of per- and polyfluoroalkyl substances (PFAS) in six different fish species from Swiss lakes |
| Fish, freshwater (tilapia, catfish, trout) | 0.03 (0.02-0.03) | µg/kg | Cyprinus carpio fillets, Switzerland 2022-2024 (N = 11); average (min-max) | PDF p.5, Table 1, PFNA row, Cyprinus carpio Av (min-max) column | Determination of per- and polyfluoroalkyl substances (PFAS) in six different fish species from Swiss lakes |
| Fish, freshwater (tilapia, catfish, trout) | 18% | µg/kg | Cyprinus carpio fillets, Switzerland 2022-2024 (N = 11); frequency of positives above LOQ | PDF p.5, Table 1, PFNA row, Cyprinus carpio F (%) column | Determination of per- and polyfluoroalkyl substances (PFAS) in six different fish species from Swiss lakes |
| Fish, freshwater (tilapia, catfish, trout) | 0.07 (0.01-0.17) | µg/kg | Oncorhynchus mykiss fillets, Switzerland 2022-2024 (N = 11); average (min-max) | PDF p.5, Table 1, PFNA row, Oncorhynchus mykiss Av (min-max) column | Determination of per- and polyfluoroalkyl substances (PFAS) in six different fish species from Swiss lakes |
| Fish, freshwater (tilapia, catfish, trout) | 20% | µg/kg | Oncorhynchus mykiss fillets, Switzerland 2022-2024 (N = 11); frequency of positives above LOQ | PDF p.5, Table 1, PFNA row, Oncorhynchus mykiss F (%) column | Determination of per- and polyfluoroalkyl substances (PFAS) in six different fish species from Swiss lakes |
| Fish, freshwater (tilapia, catfish, trout) | 0.18 (0.07-0.30) | µg/kg | Perca fluviatilis fillets, Switzerland 2022-2024 (N = 38); average (min-max) | PDF p.5, Table 1, PFNA row, Perca fluviatilis Av (min-max) column | Determination of per- and polyfluoroalkyl substances (PFAS) in six different fish species from Swiss lakes |
| Fish, freshwater (tilapia, catfish, trout) | 39% | µg/kg | Perca fluviatilis fillets, Switzerland 2022-2024 (N = 38); frequency of positives above LOQ | PDF p.5, Table 1, PFNA row, Perca fluviatilis F (%) column | Determination of per- and polyfluoroalkyl substances (PFAS) in six different fish species from Swiss lakes |
| Eggs | 0.161 | μg/kg wet weight | Backyard chicken eggs; Mean | PDF p.9 Table 2; censoring p.5 | Citizen-science data reveal drivers of PFAS variability in backyard chicken eggs |
| Eggs | 0.0122 | μg/kg wet weight | Backyard chicken eggs; SE | PDF p.9 Table 2; censoring p.5 | Citizen-science data reveal drivers of PFAS variability in backyard chicken eggs |
| Eggs | 0.070 | μg/kg wet weight | Backyard chicken eggs; Median | PDF p.9 Table 2; censoring p.5 | Citizen-science data reveal drivers of PFAS variability in backyard chicken eggs |
| Eggs | 7.90 | μg/kg wet weight | Backyard chicken eggs; Maximum | PDF p.9 Table 2; censoring p.5 | Citizen-science data reveal drivers of PFAS variability in backyard chicken eggs |
| Breast milk | 17 | pg/mL | Mother's milk, Shanghai (n = 10); average | PDF p.5, Table 1, L-PFNA row, Shanghai Conc. column | Emerging per- and polyfluoroalkyl substances (PFAS) in human milk from Sweden and China |
| Breast milk | <5-28 | pg/mL | Mother's milk, Shanghai (n = 10); range | PDF p.5, Table 1, L-PFNA row, Shanghai range in parentheses column | Emerging per- and polyfluoroalkyl substances (PFAS) in human milk from Sweden and China |
| Breast milk | 32 | pg/mL | Mother's milk, Jiaxing (n = 10); average | PDF p.5, Table 1, L-PFNA row, Jiaxing Conc. column | Emerging per- and polyfluoroalkyl substances (PFAS) in human milk from Sweden and China |
| Breast milk | 11-46 | pg/mL | Mother's milk, Jiaxing (n = 10); range | PDF p.5, Table 1, L-PFNA row, Jiaxing range in parentheses column | Emerging per- and polyfluoroalkyl substances (PFAS) in human milk from Sweden and China |
| Breast milk | 21 | pg/mL | Mother's milk, Shaoxing (n = 10); average | PDF p.5, Table 1, L-PFNA row, Shaoxing Conc. column | Emerging per- and polyfluoroalkyl substances (PFAS) in human milk from Sweden and China |
| Breast milk | 10-39 | pg/mL | Mother's milk, Shaoxing (n = 10); range | PDF p.5, Table 1, L-PFNA row, Shaoxing range in parentheses column | Emerging per- and polyfluoroalkyl substances (PFAS) in human milk from Sweden and China |
| Breast milk | 10 | pg/mL | Mother's milk, Stockholm (n = 10); average | PDF p.5, Table 1, L-PFNA row, Stockholm Conc. column | Emerging per- and polyfluoroalkyl substances (PFAS) in human milk from Sweden and China |
| Breast milk | <5-18 | pg/mL | Mother's milk, Stockholm (n = 10); range | PDF p.5, Table 1, L-PFNA row, Stockholm range in parentheses column | Emerging per- and polyfluoroalkyl substances (PFAS) in human milk from Sweden and China |
| Liquid milk, cow | ND | µg/kg | Cow bulk milk; farm F12 | PDF p.11 Table 4; limits p.10 | Preliminary Assessment of Co-Occurrence of Aflatoxin M1 and Per- and Polyfluoroalkyl Substances in Bovine and Goat Milk in Algeria |
| Liquid milk, cow | ND | µg/kg | Cow bulk milk; farm F13 | PDF p.11 Table 4; limits p.10 | Preliminary Assessment of Co-Occurrence of Aflatoxin M1 and Per- and Polyfluoroalkyl Substances in Bovine and Goat Milk in Algeria |
| Liquid milk, cow | ND | µg/kg | Cow bulk milk; farm F15 | PDF p.11 Table 4; limits p.10 | Preliminary Assessment of Co-Occurrence of Aflatoxin M1 and Per- and Polyfluoroalkyl Substances in Bovine and Goat Milk in Algeria |
| Liquid milk, cow | ND | µg/kg | Cow bulk milk; farm F19 | PDF p.11 Table 4; limits p.10 | Preliminary Assessment of Co-Occurrence of Aflatoxin M1 and Per- and Polyfluoroalkyl Substances in Bovine and Goat Milk in Algeria |
| Liquid milk, cow | ND | µg/kg | Cow bulk milk; farm F20 | PDF p.11 Table 4; limits p.10 | Preliminary Assessment of Co-Occurrence of Aflatoxin M1 and Per- and Polyfluoroalkyl Substances in Bovine and Goat Milk in Algeria |
| Liquid milk, cow | Traces | µg/kg | Cow bulk milk; farm F27 | PDF p.11 Table 4; limits p.10 | Preliminary Assessment of Co-Occurrence of Aflatoxin M1 and Per- and Polyfluoroalkyl Substances in Bovine and Goat Milk in Algeria |
| Liquid milk, cow | ND | µg/kg | Cow bulk milk; farm F36 | PDF p.11 Table 4; limits p.10 | Preliminary Assessment of Co-Occurrence of Aflatoxin M1 and Per- and Polyfluoroalkyl Substances in Bovine and Goat Milk in Algeria |
| Eggs | 0.15 ± 0.75 | ng/g wet weight | Eggs; group A1; mean ± SD if numeric | PDF p.8 Table 1 | Home-Produced Eggs as Indicators of PFAS Contamination in Food Following a Fire at a Plastic Recycling Plant |
| Eggs | 0.029 ± 0.024 | ng/g wet weight | Eggs; group A2; mean ± SD if numeric | PDF p.8 Table 1 | Home-Produced Eggs as Indicators of PFAS Contamination in Food Following a Fire at a Plastic Recycling Plant |
| Eggs | 0.022 ± 0.029 | ng/g wet weight | Eggs; group A3; mean ± SD if numeric | PDF p.8 Table 1 | Home-Produced Eggs as Indicators of PFAS Contamination in Food Following a Fire at a Plastic Recycling Plant |
| Eggs | 0.058 ± 0.045 | ng/g wet weight | Eggs; group B1; mean ± SD if numeric | PDF p.8 Table 1 | Home-Produced Eggs as Indicators of PFAS Contamination in Food Following a Fire at a Plastic Recycling Plant |
| Eggs | 0.038 ± 0.021 | ng/g wet weight | Eggs; group B2; mean ± SD if numeric | PDF p.8 Table 1 | Home-Produced Eggs as Indicators of PFAS Contamination in Food Following a Fire at a Plastic Recycling Plant |
| Eggs | 0.031 ± 0.025 | ng/g wet weight | Eggs; group B3; mean ± SD if numeric | PDF p.8 Table 1 | Home-Produced Eggs as Indicators of PFAS Contamination in Food Following a Fire at a Plastic Recycling Plant |
| Eggs | nd | ng/g wet weight | Eggs; group C1; mean ± SD if numeric | PDF p.8 Table 1 | Home-Produced Eggs as Indicators of PFAS Contamination in Food Following a Fire at a Plastic Recycling Plant |
| Eggs | nd | ng/g wet weight | Eggs; group C2/C3; mean ± SD if numeric | PDF p.8 Table 1 | Home-Produced Eggs as Indicators of PFAS Contamination in Food Following a Fire at a Plastic Recycling Plant |
| Eggs | 0.034 ± 0.022 | ng/g wet weight | Eggs; group D; mean ± SD if numeric | PDF p.8 Table 1 | Home-Produced Eggs as Indicators of PFAS Contamination in Food Following a Fire at a Plastic Recycling Plant |
| Eggs | 0.001 ± 0.006; 0.025 ± 0.003 | µg/kg | Cage eggs; mean ± SD; LB then UB where two entries | PDF p.12 Table 3; limits p.9 Table 2 | Per- and Polyfluoroalkyl Substance Levels in Commercial and Home-Produced Eggs in Croatia |
| Eggs | 0.004 ± 0.020; 0.028 ± 0.015 | µg/kg | Barn eggs; mean ± SD; LB then UB where two entries | PDF p.12 Table 3; limits p.9 Table 2 | Per- and Polyfluoroalkyl Substance Levels in Commercial and Home-Produced Eggs in Croatia |
| Eggs | 0.003 ± 0.009; 0.025 ± 0.002 | µg/kg | Organic eggs; mean ± SD; LB then UB where two entries | PDF p.12 Table 3; limits p.9 Table 2 | Per- and Polyfluoroalkyl Substance Levels in Commercial and Home-Produced Eggs in Croatia |
| Eggs | 0.027 ± 0.045; 0.041 ± 0.037 | µg/kg | Home-produced eggs; mean ± SD; LB then UB where two entries | PDF p.12 Table 3; limits p.9 Table 2 | Per- and Polyfluoroalkyl Substance Levels in Commercial and Home-Produced Eggs in Croatia |
| Meat and poultry | 0.22 | µg/kg fresh weight | Wild boar meat, Germany (n = 152); mean | PDF p.4, Table 2, Wild boar meat block, PFNA row, Mean column | An assessment of PFAS contamination in wild boar meat and liver |
| Meat and poultry | 0.03 | µg/kg fresh weight | Wild boar meat, Germany (n = 152); median | PDF p.4, Table 2, Wild boar meat block, PFNA row, Median column | An assessment of PFAS contamination in wild boar meat and liver |
| Meat and poultry | 4.60 | µg/kg fresh weight | Wild boar meat, Germany (n = 152); maximum | PDF p.4, Table 2, Wild boar meat block, PFNA row, Max column | An assessment of PFAS contamination in wild boar meat and liver |
| Meat and poultry | 17.07 | µg/kg fresh weight | Wild boar liver, Germany (n = 114); mean | PDF p.4, Table 2, Wild boar liver block, PFNA row, Mean column | An assessment of PFAS contamination in wild boar meat and liver |
| Meat and poultry | 9.25 | µg/kg fresh weight | Wild boar liver, Germany (n = 114); median | PDF p.4, Table 2, Wild boar liver block, PFNA row, Median column | An assessment of PFAS contamination in wild boar meat and liver |
| Meat and poultry | 273.00 | µg/kg fresh weight | Wild boar liver, Germany (n = 114); maximum | PDF p.4, Table 2, Wild boar liver block, PFNA row, Max column | An assessment of PFAS contamination in wild boar meat and liver |
| Bottled drinking water (purified, spring, artesian) | 0.08 | ng/L | bottled-water mean as printed; non-detect mean retained literally | PDF p. 8, Table 1, Bottled Water Mean | Unregulated and Regulated PFASs in Bottled and Tap Water: Occurrence, Co-Occurrence Patterns, and Implications for Human Health and Regulatory Frameworks |
| Breast milk | <LOD | ng/mL | Human milk, New Hampshire Birth Cohort Study (N = 426); median [IQR] | PDF p.4, Table 2, PFNA row, milk median (IQR) column | Concentrations of Per- and Polyfluoroalkyl Substances in Paired Maternal Plasma and Human Milk in the New Hampshire Birth Cohort |
| Breast milk | 29 (6.8) | ng/mL | Human milk, New Hampshire Birth Cohort Study (N = 426); samples at or above LOD, N (%) | PDF p.4, Table 2, PFNA row, milk N (% >= LOD) column | Concentrations of Per- and Polyfluoroalkyl Substances in Paired Maternal Plasma and Human Milk in the New Hampshire Birth Cohort |
| Meat and poultry | 0.040-0.138 | µg/kg | Pig liver, Italy; concentration range | PDF p.3, Table 1, Liver block, PFNA row, Concentration range column | Distribution of poly- and perfluoroalkyl substances in pig liver and muscle: implications for food safety |
| Meat and poultry | 0.026 | µg/kg | Pig liver, Italy; mean | PDF p.3, Table 1, Liver block, PFNA row, Mean column | Distribution of poly- and perfluoroalkyl substances in pig liver and muscle: implications for food safety |
| Meat and poultry | 0.000 | µg/kg | Pig liver, Italy; median | PDF p.3, Table 1, Liver block, PFNA row, Median column | Distribution of poly- and perfluoroalkyl substances in pig liver and muscle: implications for food safety |
| Liquid milk, cow | 0.43 ± 0.66 | pg g−1 | Raw cow milk fraction Skimmed; mean ± SD | PDF p.6 Table 2 | First Investigation of the Physiological Distribution of Legacy and Emerging Perfluoroalkyl Substances in Raw Bovine Milk According to the Component Fraction |
| Liquid milk, cow | 1.00 ± 1.40 | pg g−1 | Raw cow milk fraction Cream; mean ± SD | PDF p.6 Table 2 | First Investigation of the Physiological Distribution of Legacy and Emerging Perfluoroalkyl Substances in Raw Bovine Milk According to the Component Fraction |
| Tap drinking water | 56 | ng/L | maximum in reused public-supply monitoring data | PDF p3, Results and Discussion, paragraph beginning Six million | Detection of Poly- and Perfluoroalkyl Substances (PFASs) in U.S. Drinking Water Linked to Industrial Sites, Military Fire Training Areas, and Wastewater Treatment Plants |
| Tap drinking water | 0.28 | ng/L | drinking-water sample D1 | PDF p3, Table 1, D1 row | Presence of Emerging Per- and Polyfluoroalkyl Substances (PFASs) in River and Drinking Water near a Fluorochemical Production Plant in the Netherlands |
| Tap drinking water | 0.25 | ng/L | drinking-water sample D2 | PDF p3, Table 1, D2 row | Presence of Emerging Per- and Polyfluoroalkyl Substances (PFASs) in River and Drinking Water near a Fluorochemical Production Plant in the Netherlands |
| Tap drinking water | 0.09 | ng/L | drinking-water sample D3 | PDF p3, Table 1, D3 row | Presence of Emerging Per- and Polyfluoroalkyl Substances (PFASs) in River and Drinking Water near a Fluorochemical Production Plant in the Netherlands |
| Tap drinking water | <0.03 | ng/L | drinking-water sample D4 | PDF p3, Table 1, D4 row | Presence of Emerging Per- and Polyfluoroalkyl Substances (PFASs) in River and Drinking Water near a Fluorochemical Production Plant in the Netherlands |
| Tap drinking water | <0.03 | ng/L | drinking-water sample D5 | PDF p3, Table 1, D5 row | Presence of Emerging Per- and Polyfluoroalkyl Substances (PFASs) in River and Drinking Water near a Fluorochemical Production Plant in the Netherlands |
| Tap drinking water | <0.03 | ng/L | drinking-water sample D6 | PDF p3, Table 1, D6 row | Presence of Emerging Per- and Polyfluoroalkyl Substances (PFASs) in River and Drinking Water near a Fluorochemical Production Plant in the Netherlands |
| Tap drinking water | 0.23 (0.13, 0.29) | ng/L | median (IQR), detected archived tap-water samples only | PDF p3, Table 2, nPFNA | Tap Water Contributions to Plasma Concentrations of Poly- and Perfluoroalkyl Substances (PFAS) in a Nationwide Prospective Cohort of U.S. Women |
| Tap drinking water | 0.19 (0.10, 0.34) | ng/L | median (IQR), detected archived tap-water samples only | PDF p3, Table 2, brPFNA | Tap Water Contributions to Plasma Concentrations of Poly- and Perfluoroalkyl Substances (PFAS) in a Nationwide Prospective Cohort of U.S. Women |
| Tap drinking water | <LOQ | ng/L | unfiltered tap water; median [min, max] among quantifiable results or printed <LOQ | PDF p3, Table 2, unfiltered tap-water column | Concentrations of per- and polyfluoroalkyl substances (PFAS) in paired tap water and blood samples during pregnancy |
| Tap drinking water | 0.26 [0.03, 0.4] | ng/L | surface-water-derived produced drinking water; median [min, max], including source censoring treatment | PDF p5, Table 2, surface-water-derived drinking-water column | Occurrence, Fate, and Related Health Risks of PFAS in Raw and Produced Drinking Water |
| Tap drinking water | 0.03 [0.03, 0.09] | ng/L | groundwater-derived produced drinking water; median [min, max], including source censoring treatment | PDF p5, Table 2, groundwater-derived drinking-water column | Occurrence, Fate, and Related Health Risks of PFAS in Raw and Produced Drinking Water |
| Tap drinking water | 0.1-1.6 | ng/L | drinking-water application samples; content range or single reported value | PDF p11, Table 5, Drinking water Content column | Determination of 51 per- and polyfluoroalkyl substances in raw water and drinking water by online solid-phase extraction coupled with ultra performance liquid chromatography-tandem mass spectrometry |
| Paperboard cartons | below their respective LOQs | µg/kg | Migration into all four simulants under standardized conditions | PDF p.7, section 2.3.2 and Figure 3 caption | Migration Safety of Perfluoroalkyl Substances from Sugarcane Pulp Tableware: Residue Analysis and Takeout Simulation Study |
| Eggs | traces | ng/g | Homogenized egg yolk; group C pool 2 | PDF p.3 Table 3; limits p.2 | Preliminary monitoring of the presence of perfluoroalkyl substances in Italian eggs from different breeding systems |
| Liquid milk, cow | < MDL-10.4 | pg/g | Farm tank cow milk; range | PDF p.5 Results, left column | Occurrence of PFAS in Cow’s Milk: A Comparative Study of Swedish Farms near Contaminated Sites and Regional Dairy Production Facilities |
| Liquid milk, cow | < MDL | pg/g | Regional dairy production facility silo milk | PDF p.1 Abstract; p.6 Dairy Production Facilities Samples | Occurrence of PFAS in Cow’s Milk: A Comparative Study of Swedish Farms near Contaminated Sites and Regional Dairy Production Facilities |
| Breast milk | n.d.-15 | ng/L | Breast milk, Austria, follow-up study 2014-2016 (n = 40); range | PDF p.11, Table 3, follow-up study block, PFNA row, follow-up range column | Persistent Organic Pollutants in Austrian Human Breast Milk Collected between 2013 and 2016 |
| Breast milk | <LOQ | ng/L | Breast milk, Austria, follow-up study 2014-2016 (n = 40); median | PDF p.11, Table 3, follow-up study block, PFNA row, follow-up median column | Persistent Organic Pollutants in Austrian Human Breast Milk Collected between 2013 and 2016 |
| Breast milk | 8.0 | ng/L | Breast milk, Austria, follow-up study 2014-2016 (n = 40); 95th percentile | PDF p.11, Table 3, follow-up study block, PFNA row, follow-up P95 column | Persistent Organic Pollutants in Austrian Human Breast Milk Collected between 2013 and 2016 |
| Carpet cleaners | 0 | % | German consumer products, Cleaner samples (percentage with detected PFAS); percentage of samples detected | PDF p.7, Table 3, PFNA row, Cleaner column | Perfluoroalkyl and polyfluoroalkyl substances in consumer products |
| Textiles, apparel and outdoor gear | 67 | % | German consumer products, Outdoor samples (percentage with detected PFAS); percentage of samples detected | PDF p.7, Table 3, PFNA row, Outdoor column | Perfluoroalkyl and polyfluoroalkyl substances in consumer products |
| Carpet cleaners | 20 | % | German consumer products, Carpet samples (percentage with detected PFAS); percentage of samples detected | PDF p.7, Table 3, PFNA row, Carpet column | Perfluoroalkyl and polyfluoroalkyl substances in consumer products |
| Breast milk | 0.16 | ng/mL | Human milk, e-waste dismantling area, China (n = 150); maximum | PDF p.6, Table 2, PFNA row, Max column | Association Between Prenatal Exposure to Per‐ and Poly‐Fluoroalkyl Substances From Electronic Waste Disassembly Areas and Steroid Hormones in Human Milk Samples |
| Breast milk | <LOD | ng/mL | Human milk, e-waste dismantling area, China (n = 150); median | PDF p.6, Table 2, PFNA row, Median column | Association Between Prenatal Exposure to Per‐ and Poly‐Fluoroalkyl Substances From Electronic Waste Disassembly Areas and Steroid Hormones in Human Milk Samples |
| Breast milk | 0.01 | ng/mL | Human milk, e-waste dismantling area, China (n = 150); mean | PDF p.6, Table 2, PFNA row, Mean column | Association Between Prenatal Exposure to Per‐ and Poly‐Fluoroalkyl Substances From Electronic Waste Disassembly Areas and Steroid Hormones in Human Milk Samples |
| Breast milk | 10.0 | ng/mL | Human milk, e-waste dismantling area, China (n = 150); detection frequency (%) | PDF p.6, Table 2, PFNA row, Detection frequencies column | Association Between Prenatal Exposure to Per‐ and Poly‐Fluoroalkyl Substances From Electronic Waste Disassembly Areas and Steroid Hormones in Human Milk Samples |
| Seafood | 49% | µg/kg | Singapore total diet study, Fish and seafood (n = 93 pooled samples); detection rate | PDF p.8, Table 4, Fish and seafood block, PFNA row, Fish and seafood Detection column | Occurrence and Dietary Exposure of PFAS in Singapore: Insights from a Total Diet Study |
| Seafood | 0.03 ± 0.08 | µg/kg | Singapore total diet study, Fish and seafood (n = 93 pooled samples); mean (lower bound) ± SD | PDF p.8, Table 4, Fish and seafood block, PFNA row, Fish and seafood Mean (LB) column | Occurrence and Dietary Exposure of PFAS in Singapore: Insights from a Total Diet Study |
| Condiments (hot sauce, soy sauce, mustard, ketchup, mayonnaise, salsa) | 0% | µg/kg | Singapore total diet study, Sauces and condiments (n = 18 pooled samples); detection rate | PDF p.8, Table 4, Sauces and condiments block, PFNA row, Sauces and condiments Detection column | Occurrence and Dietary Exposure of PFAS in Singapore: Insights from a Total Diet Study |
| Condiments (hot sauce, soy sauce, mustard, ketchup, mayonnaise, salsa) | 0.00 ± 0.00 | µg/kg | Singapore total diet study, Sauces and condiments (n = 18 pooled samples); mean (lower bound) ± SD | PDF p.8, Table 4, Sauces and condiments block, PFNA row, Sauces and condiments Mean (LB) column | Occurrence and Dietary Exposure of PFAS in Singapore: Insights from a Total Diet Study |
| Eggs | 13% | µg/kg | Singapore total diet study, Eggs and egg products (n = 14 pooled samples); detection rate | PDF p.8, Table 4, Eggs and egg products block, PFNA row, Eggs and egg products Detection column | Occurrence and Dietary Exposure of PFAS in Singapore: Insights from a Total Diet Study |
| Eggs | 0.00 ± 0.00 | µg/kg | Singapore total diet study, Eggs and egg products (n = 14 pooled samples); mean (lower bound) ± SD | PDF p.8, Table 4, Eggs and egg products block, PFNA row, Eggs and egg products Mean (LB) column | Occurrence and Dietary Exposure of PFAS in Singapore: Insights from a Total Diet Study |
| Meat and poultry | 2% | µg/kg | Singapore total diet study, Meat and meat products (n = 53 pooled samples); detection rate | PDF p.8, Table 4, Meat and meat products block, PFNA row, Meat and meat products Detection column | Occurrence and Dietary Exposure of PFAS in Singapore: Insights from a Total Diet Study |
| Meat and poultry | 0.00 ± 0.00 | µg/kg | Singapore total diet study, Meat and meat products (n = 53 pooled samples); mean (lower bound) ± SD | PDF p.8, Table 4, Meat and meat products block, PFNA row, Meat and meat products Mean (LB) column | Occurrence and Dietary Exposure of PFAS in Singapore: Insights from a Total Diet Study |
| Bottled drinking water (purified, spring, artesian) | 0.4 | ng/L | one quantified natural-mineral bottled-water sample | PDF p. 10 (56545), Occurrence in bottled water samples | Occurrence and health risk assessment of PFAS and possible precursors: a case study in a drinking water treatment plant and bottled water (south Catalonia, Spain) |
| Liquid milk, cow | 0.0015 | µg/kg | Cow milk; source table mean | PDF p.5 Tables 1 to 2 | Occurrence of perfluoroalkyl substances in cow’s, goat’s and sheep’s milk - dietary intake and risk assessment |
| Liquid milk, cow | 0.0015 | µg/kg | Cow milk; source table median | PDF p.5 Tables 1 to 2 | Occurrence of perfluoroalkyl substances in cow’s, goat’s and sheep’s milk - dietary intake and risk assessment |
| Liquid milk, cow | <LOQ-0.0016 | µg/kg | Cow milk; source table range | PDF p.5 Tables 1 to 2 | Occurrence of perfluoroalkyl substances in cow’s, goat’s and sheep’s milk - dietary intake and risk assessment |
| Eggs | 0.031 | µg/kg | Chickens eggs; source table mean | PDF p.4 Tables 2 to 3; LOQs p.3 Table 1 | Chickens’ eggs and the livers of farm animals as sources of perfluoroalkyl substances |
| Eggs | n.d. | ng g−1 | Homogenized commercial egg; sample 1 | PDF p.9 Table 3; LOQ p.5 Table 2 | Incidence of Perfluoroalkyl Substances in Commercial Eggs and Their Impact on Consumer’s Safety |
| Eggs | n.d. | ng g−1 | Homogenized commercial egg; sample 2 | PDF p.9 Table 3; LOQ p.5 Table 2 | Incidence of Perfluoroalkyl Substances in Commercial Eggs and Their Impact on Consumer’s Safety |
| Eggs | n.d. | ng g−1 | Homogenized commercial egg; sample 3 | PDF p.9 Table 3; LOQ p.5 Table 2 | Incidence of Perfluoroalkyl Substances in Commercial Eggs and Their Impact on Consumer’s Safety |
| Eggs | n.d. | ng g−1 | Homogenized commercial egg; sample 4 | PDF p.9 Table 3; LOQ p.5 Table 2 | Incidence of Perfluoroalkyl Substances in Commercial Eggs and Their Impact on Consumer’s Safety |
| Eggs | n.d. | ng g−1 | Homogenized commercial egg; sample 5 | PDF p.9 Table 3; LOQ p.5 Table 2 | Incidence of Perfluoroalkyl Substances in Commercial Eggs and Their Impact on Consumer’s Safety |
| Eggs | n.d. | ng g−1 | Homogenized commercial egg; sample 6 | PDF p.9 Table 3; LOQ p.5 Table 2 | Incidence of Perfluoroalkyl Substances in Commercial Eggs and Their Impact on Consumer’s Safety |
| Eggs | n.d. | ng g−1 | Homogenized commercial egg; sample 7 | PDF p.9 Table 3; LOQ p.5 Table 2 | Incidence of Perfluoroalkyl Substances in Commercial Eggs and Their Impact on Consumer’s Safety |
| Eggs | n.d. | ng g−1 | Homogenized commercial egg; sample 8 | PDF p.9 Table 3; LOQ p.5 Table 2 | Incidence of Perfluoroalkyl Substances in Commercial Eggs and Their Impact on Consumer’s Safety |
| Eggs | n.d. | ng g−1 | Homogenized commercial egg; sample 9 | PDF p.9 Table 3; LOQ p.5 Table 2 | Incidence of Perfluoroalkyl Substances in Commercial Eggs and Their Impact on Consumer’s Safety |
| Eggs | n.d. | ng g−1 | Homogenized commercial egg; sample 10 | PDF p.9 Table 3; LOQ p.5 Table 2 | Incidence of Perfluoroalkyl Substances in Commercial Eggs and Their Impact on Consumer’s Safety |
| Eggs | n.d. | ng g−1 | Homogenized commercial egg; sample 11 | PDF p.9 Table 3; LOQ p.5 Table 2 | Incidence of Perfluoroalkyl Substances in Commercial Eggs and Their Impact on Consumer’s Safety |
| Eggs | n.d. | ng g−1 | Homogenized commercial egg; sample 12 | PDF p.9 Table 3; LOQ p.5 Table 2 | Incidence of Perfluoroalkyl Substances in Commercial Eggs and Their Impact on Consumer’s Safety |
| Eggs | n.d. | ng g−1 | Homogenized commercial egg; sample 13 | PDF p.9 Table 3; LOQ p.5 Table 2 | Incidence of Perfluoroalkyl Substances in Commercial Eggs and Their Impact on Consumer’s Safety |
| Eggs | n.d. | ng g−1 | Homogenized commercial egg; sample 14 | PDF p.9 Table 3; LOQ p.5 Table 2 | Incidence of Perfluoroalkyl Substances in Commercial Eggs and Their Impact on Consumer’s Safety |
| Eggs | n.d. | ng g−1 | Homogenized commercial egg; sample 15 | PDF p.9 Table 3; LOQ p.5 Table 2 | Incidence of Perfluoroalkyl Substances in Commercial Eggs and Their Impact on Consumer’s Safety |
| Eggs | n.d. | ng g−1 | Homogenized commercial egg; sample 16 | PDF p.9 Table 3; LOQ p.5 Table 2 | Incidence of Perfluoroalkyl Substances in Commercial Eggs and Their Impact on Consumer’s Safety |
| Eggs | n.d. | ng g−1 | Homogenized commercial egg; sample 17 | PDF p.9 Table 3; LOQ p.5 Table 2 | Incidence of Perfluoroalkyl Substances in Commercial Eggs and Their Impact on Consumer’s Safety |
| Eggs | n.d. | ng g−1 | Homogenized commercial egg; sample 18 | PDF p.9 Table 3; LOQ p.5 Table 2 | Incidence of Perfluoroalkyl Substances in Commercial Eggs and Their Impact on Consumer’s Safety |
| Eggs | n.d. | ng g−1 | Homogenized commercial egg; sample 19 | PDF p.9 Table 3; LOQ p.5 Table 2 | Incidence of Perfluoroalkyl Substances in Commercial Eggs and Their Impact on Consumer’s Safety |
| Eggs | n.d. | ng g−1 | Homogenized commercial egg; sample 20 | PDF p.9 Table 3; LOQ p.5 Table 2 | Incidence of Perfluoroalkyl Substances in Commercial Eggs and Their Impact on Consumer’s Safety |
| Eggs | n.d. | ng g−1 | Homogenized commercial egg; sample 21 | PDF p.9 Table 3; LOQ p.5 Table 2 | Incidence of Perfluoroalkyl Substances in Commercial Eggs and Their Impact on Consumer’s Safety |
| Eggs | n.d. | ng g−1 | Homogenized commercial egg; sample 22 | PDF p.9 Table 3; LOQ p.5 Table 2 | Incidence of Perfluoroalkyl Substances in Commercial Eggs and Their Impact on Consumer’s Safety |
| Eggs | n.d. | ng g−1 | Homogenized commercial egg; sample 23 | PDF p.9 Table 3; LOQ p.5 Table 2 | Incidence of Perfluoroalkyl Substances in Commercial Eggs and Their Impact on Consumer’s Safety |
| Eggs | n.d. | ng g−1 | Homogenized commercial egg; sample 24 | PDF p.9 Table 3; LOQ p.5 Table 2 | Incidence of Perfluoroalkyl Substances in Commercial Eggs and Their Impact on Consumer’s Safety |
| Eggs | n.d. | ng g−1 | Homogenized commercial egg; sample 25 | PDF p.9 Table 3; LOQ p.5 Table 2 | Incidence of Perfluoroalkyl Substances in Commercial Eggs and Their Impact on Consumer’s Safety |
| Eggs | n.d. | ng g−1 | Homogenized commercial egg; sample 26 | PDF p.9 Table 3; LOQ p.5 Table 2 | Incidence of Perfluoroalkyl Substances in Commercial Eggs and Their Impact on Consumer’s Safety |
| Eggs | n.d. | ng g−1 | Homogenized commercial egg; sample 27 | PDF p.9 Table 3; LOQ p.5 Table 2 | Incidence of Perfluoroalkyl Substances in Commercial Eggs and Their Impact on Consumer’s Safety |
| Eggs | n.d. | ng g−1 | Homogenized commercial egg; sample 28 | PDF p.9 Table 3; LOQ p.5 Table 2 | Incidence of Perfluoroalkyl Substances in Commercial Eggs and Their Impact on Consumer’s Safety |
| Eggs | <LOQ | ng g−1 | Homogenized commercial egg; sample 29 | PDF p.9 Table 3; LOQ p.5 Table 2 | Incidence of Perfluoroalkyl Substances in Commercial Eggs and Their Impact on Consumer’s Safety |
| Eggs | n.d. | ng g−1 | Homogenized commercial egg; sample 30 | PDF p.9 Table 3; LOQ p.5 Table 2 | Incidence of Perfluoroalkyl Substances in Commercial Eggs and Their Impact on Consumer’s Safety |
| Eggs | n.d. | ng g−1 | Homogenized commercial egg; sample 31 | PDF p.10 Table 3; LOQ p.5 Table 2 | Incidence of Perfluoroalkyl Substances in Commercial Eggs and Their Impact on Consumer’s Safety |
| Eggs | n.d. | ng g−1 | Homogenized commercial egg; sample 32 | PDF p.10 Table 3; LOQ p.5 Table 2 | Incidence of Perfluoroalkyl Substances in Commercial Eggs and Their Impact on Consumer’s Safety |
| Eggs | n.d. | ng g−1 | Homogenized commercial egg; sample 33 | PDF p.10 Table 3; LOQ p.5 Table 2 | Incidence of Perfluoroalkyl Substances in Commercial Eggs and Their Impact on Consumer’s Safety |
| Eggs | n.d. | ng g−1 | Homogenized commercial egg; sample 34 | PDF p.10 Table 3; LOQ p.5 Table 2 | Incidence of Perfluoroalkyl Substances in Commercial Eggs and Their Impact on Consumer’s Safety |
| Eggs | n.d. | ng g−1 | Homogenized commercial egg; sample 35 | PDF p.10 Table 3; LOQ p.5 Table 2 | Incidence of Perfluoroalkyl Substances in Commercial Eggs and Their Impact on Consumer’s Safety |
| Eggs | n.d. | ng g−1 | Homogenized commercial egg; sample 36 | PDF p.10 Table 3; LOQ p.5 Table 2 | Incidence of Perfluoroalkyl Substances in Commercial Eggs and Their Impact on Consumer’s Safety |
| Eggs | n.d. | ng g−1 | Homogenized commercial egg; sample 37 | PDF p.10 Table 3; LOQ p.5 Table 2 | Incidence of Perfluoroalkyl Substances in Commercial Eggs and Their Impact on Consumer’s Safety |
| Eggs | <LOQ | ng g−1 | Homogenized commercial egg; sample 38 | PDF p.10 Table 3; LOQ p.5 Table 2 | Incidence of Perfluoroalkyl Substances in Commercial Eggs and Their Impact on Consumer’s Safety |
| Eggs | n.d. | ng g−1 | Homogenized commercial egg; sample 39 | PDF p.10 Table 3; LOQ p.5 Table 2 | Incidence of Perfluoroalkyl Substances in Commercial Eggs and Their Impact on Consumer’s Safety |
| Eggs | n.d. | ng g−1 | Homogenized commercial egg; sample 40 | PDF p.10 Table 3; LOQ p.5 Table 2 | Incidence of Perfluoroalkyl Substances in Commercial Eggs and Their Impact on Consumer’s Safety |
| Eggs | n.d. | ng g−1 | Homogenized commercial egg; sample 41 | PDF p.10 Table 3; LOQ p.5 Table 2 | Incidence of Perfluoroalkyl Substances in Commercial Eggs and Their Impact on Consumer’s Safety |
| Eggs | <LOQ | ng g−1 | Homogenized commercial egg; sample 42 | PDF p.10 Table 3; LOQ p.5 Table 2 | Incidence of Perfluoroalkyl Substances in Commercial Eggs and Their Impact on Consumer’s Safety |
| Eggs | n.d. | ng g−1 | Homogenized commercial egg; sample 43 | PDF p.10 Table 3; LOQ p.5 Table 2 | Incidence of Perfluoroalkyl Substances in Commercial Eggs and Their Impact on Consumer’s Safety |
| Eggs | n.d. | ng g−1 | Homogenized commercial egg; sample 44 | PDF p.10 Table 3; LOQ p.5 Table 2 | Incidence of Perfluoroalkyl Substances in Commercial Eggs and Their Impact on Consumer’s Safety |
| Eggs | n.d. | ng g−1 | Homogenized commercial egg; sample 45 | PDF p.10 Table 3; LOQ p.5 Table 2 | Incidence of Perfluoroalkyl Substances in Commercial Eggs and Their Impact on Consumer’s Safety |
| Eggs | n.d. | ng g−1 | Homogenized commercial egg; sample 46 | PDF p.10 Table 3; LOQ p.5 Table 2 | Incidence of Perfluoroalkyl Substances in Commercial Eggs and Their Impact on Consumer’s Safety |
| Eggs | n.d. | ng g−1 | Homogenized commercial egg; sample 47 | PDF p.10 Table 3; LOQ p.5 Table 2 | Incidence of Perfluoroalkyl Substances in Commercial Eggs and Their Impact on Consumer’s Safety |
| Eggs | n.d. | ng g−1 | Homogenized commercial egg; sample 48 | PDF p.10 Table 3; LOQ p.5 Table 2 | Incidence of Perfluoroalkyl Substances in Commercial Eggs and Their Impact on Consumer’s Safety |
| Eggs | n.d. | ng g−1 | Homogenized commercial egg; sample 49 | PDF p.10 Table 3; LOQ p.5 Table 2 | Incidence of Perfluoroalkyl Substances in Commercial Eggs and Their Impact on Consumer’s Safety |
| Eggs | n.d. | ng g−1 | Homogenized commercial egg; sample 50 | PDF p.10 Table 3; LOQ p.5 Table 2 | Incidence of Perfluoroalkyl Substances in Commercial Eggs and Their Impact on Consumer’s Safety |
| Eggs | n.d. | ng g−1 | Homogenized commercial egg; sample 51 | PDF p.10 Table 3; LOQ p.5 Table 2 | Incidence of Perfluoroalkyl Substances in Commercial Eggs and Their Impact on Consumer’s Safety |
| Eggs | n.d. | ng g−1 | Homogenized commercial egg; sample 52 | PDF p.10 Table 3; LOQ p.5 Table 2 | Incidence of Perfluoroalkyl Substances in Commercial Eggs and Their Impact on Consumer’s Safety |
| Eggs | n.d. | ng g−1 | Homogenized commercial egg; sample 53 | PDF p.10 Table 3; LOQ p.5 Table 2 | Incidence of Perfluoroalkyl Substances in Commercial Eggs and Their Impact on Consumer’s Safety |
| Eggs | n.d. | ng g−1 | Homogenized commercial egg; sample 54 | PDF p.10 Table 3; LOQ p.5 Table 2 | Incidence of Perfluoroalkyl Substances in Commercial Eggs and Their Impact on Consumer’s Safety |
| Eggs | n.d. | ng g−1 | Homogenized commercial egg; sample 55 | PDF p.10 Table 3; LOQ p.5 Table 2 | Incidence of Perfluoroalkyl Substances in Commercial Eggs and Their Impact on Consumer’s Safety |
| Eggs | n.d. | ng g−1 | Homogenized commercial egg; sample 56 | PDF p.10 Table 3; LOQ p.5 Table 2 | Incidence of Perfluoroalkyl Substances in Commercial Eggs and Their Impact on Consumer’s Safety |
| Eggs | n.d. | ng g−1 | Homogenized commercial egg; sample 57 | PDF p.10 Table 3; LOQ p.5 Table 2 | Incidence of Perfluoroalkyl Substances in Commercial Eggs and Their Impact on Consumer’s Safety |
| Eggs | n.d. | ng g−1 | Homogenized commercial egg; sample 58 | PDF p.10 Table 3; LOQ p.5 Table 2 | Incidence of Perfluoroalkyl Substances in Commercial Eggs and Their Impact on Consumer’s Safety |
| Eggs | n.d. | ng g−1 | Homogenized commercial egg; sample 59 | PDF p.10 Table 3; LOQ p.5 Table 2 | Incidence of Perfluoroalkyl Substances in Commercial Eggs and Their Impact on Consumer’s Safety |
| Eggs | n.d. | ng g−1 | Homogenized commercial egg; sample 60 | PDF p.10 Table 3; LOQ p.5 Table 2 | Incidence of Perfluoroalkyl Substances in Commercial Eggs and Their Impact on Consumer’s Safety |
| Eggs | n.d. | ng g−1 | Homogenized commercial egg; sample 61 | PDF p.10 Table 3; LOQ p.5 Table 2 | Incidence of Perfluoroalkyl Substances in Commercial Eggs and Their Impact on Consumer’s Safety |
| Eggs | n.d. | ng g−1 | Homogenized commercial egg; sample 62 | PDF p.10 Table 3; LOQ p.5 Table 2 | Incidence of Perfluoroalkyl Substances in Commercial Eggs and Their Impact on Consumer’s Safety |
| Eggs | n.d. | ng g−1 | Homogenized commercial egg; sample 63 | PDF p.10 Table 3; LOQ p.5 Table 2 | Incidence of Perfluoroalkyl Substances in Commercial Eggs and Their Impact on Consumer’s Safety |
| Eggs | n.d. | ng g−1 | Homogenized commercial egg; sample 64 | PDF p.10 Table 3; LOQ p.5 Table 2 | Incidence of Perfluoroalkyl Substances in Commercial Eggs and Their Impact on Consumer’s Safety |
| Eggs | n.d. | ng g−1 | Homogenized commercial egg; sample 65 | PDF p.10 Table 3; LOQ p.5 Table 2 | Incidence of Perfluoroalkyl Substances in Commercial Eggs and Their Impact on Consumer’s Safety |
| Children's products | 83 | µg/m² | Stuffed toys, PFAS migration (not total content); detection frequency (%) | PDF p.5, Table 1, PFNA row, DF (%) column | Stuffed toys as a source of oral PFAS exposure: Migration into artificial saliva and exposure assessment |
| Children's products | 0.03 | µg/m² | Stuffed toys, PFAS migration (not total content); mean migration (as reported) | PDF p.5, Table 1, PFNA row, Mean [μg/m²] column | Stuffed toys as a source of oral PFAS exposure: Migration into artificial saliva and exposure assessment |
| Children's products | <LOQ - 0.11 | µg/m² | Stuffed toys, PFAS migration (not total content); range of migration | PDF p.5, Table 1, PFNA row, Range [μg/m²] column | Stuffed toys as a source of oral PFAS exposure: Migration into artificial saliva and exposure assessment |
| Breast milk | <LOD - 396 | ng/L | Canadian human milk (MIREC, n = 664); range | PDF p.5, Table 3, PFNA row, Range column | Perfluorinated alkyl substances in Canadian human milk as part of the Maternal-Infant Research on Environmental Chemicals (MIREC) study |
| Breast milk | 10.4 | ng/L | Canadian human milk (MIREC, n = 664); mean of results above LOD | PDF p.5, Table 3, PFNA row, Mean, >LOD only column | Perfluorinated alkyl substances in Canadian human milk as part of the Maternal-Infant Research on Environmental Chemicals (MIREC) study |
| Breast milk | 7.60 | ng/L | Canadian human milk (MIREC, n = 664); median of results above LOD | PDF p.5, Table 3, PFNA row, Median, >LOD only column | Perfluorinated alkyl substances in Canadian human milk as part of the Maternal-Infant Research on Environmental Chemicals (MIREC) study |
| Breast milk | 61.0 | % | Canadian human milk (MIREC, n = 664); detection frequency | PDF p.5, Table 3, PFNA row, Detection frequency column | Perfluorinated alkyl substances in Canadian human milk as part of the Maternal-Infant Research on Environmental Chemicals (MIREC) study |
| Children's products | 1.6% (1/61) | % | Children's and bedding textile products, US (n = 61, targeted analysis); detection frequency (detected/analyzed) | PDF p.5, Table 3, PFNA row, targeted, number of detections column | How Well Do Product Labels Indicate the Presence of PFAS in Consumer Items Used by Children and Adolescents? |
| Children's products | 1.62 | ng/g | same; maximum | PDF p.5, Table 3, PFNA row, targeted, maximum concentration (ng/g) column | How Well Do Product Labels Indicate the Presence of PFAS in Consumer Items Used by Children and Adolescents? |
| Children's products | 0.015 | ng/cm2 | same; maximum | PDF p.5, Table 3, PFNA row, targeted, maximum concentration (ng/cm2) column | How Well Do Product Labels Indicate the Presence of PFAS in Consumer Items Used by Children and Adolescents? |
| Bottled drinking water (purified, spring, artesian) | 0.16 | ng/L | bottled-water mean based on detections above MDL; ND literal | PDF p. 4 (4398), Table 1 bottled-water mean and footnotes a/f | Tap vs Bottled: Assessing PFAS Levels and Exposure Risks in Singapore’s Drinking Water |
| Textiles, apparel and outdoor gear | 16.0 | ng/g | Children's products, China, School uniform (n = 25); detection frequency (%) | PDF p.5, Table 1, PFNA row, School uniform DF column | Per- and Polyfluoroalkyl Substances in North American School Uniforms |
| Textiles, apparel and outdoor gear | ND-0.293 | ng/g | Children's products, China, School uniform (n = 25); range | PDF p.5, Table 1, PFNA row, School uniform Range column | Per- and Polyfluoroalkyl Substances in North American School Uniforms |
| Textiles, apparel and outdoor gear | 56.3 | ng/g | Children's products, China, Outdoor wear (n = 16); detection frequency (%) | PDF p.5, Table 1, PFNA row, Outdoor wear DF column | Per- and Polyfluoroalkyl Substances in North American School Uniforms |
| Textiles, apparel and outdoor gear | 0.168 | ng/g | Children's products, China, Outdoor wear (n = 16); median (non-detects set to 1/2 MDL) | PDF p.5, Table 1, PFNA row, Outdoor wear Median column | Per- and Polyfluoroalkyl Substances in North American School Uniforms |
| Textiles, apparel and outdoor gear | ND-1.25 | ng/g | Children's products, China, Outdoor wear (n = 16); range | PDF p.5, Table 1, PFNA row, Outdoor wear Range column | Per- and Polyfluoroalkyl Substances in North American School Uniforms |
| Children's products | 37.5 | ng/g | Children's products, China, Miscellaneous (n = 16); detection frequency (%) | PDF p.5, Table 1, PFNA row, Miscellaneous DF column | Per- and Polyfluoroalkyl Substances in North American School Uniforms |
| Children's products | ND-0.532 | ng/g | Children's products, China, Miscellaneous (n = 16); range | PDF p.5, Table 1, PFNA row, Miscellaneous Range column | Per- and Polyfluoroalkyl Substances in North American School Uniforms |
| Breast milk | 100 | ng/L | Human milk, China (n = 1,151); detection rate (%) | PDF p.6, Table 2, PFNA row, DR (%) column | Emerging and Legacy Perfluoroalkyl Substances in Breastfed Chinese Infants: Renal Clearance, Body Burden, and Implications |
| Breast milk | 1.161 | ng/L | Human milk, China (n = 1,151); minimum | PDF p.6, Table 2, PFNA row, Min column | Emerging and Legacy Perfluoroalkyl Substances in Breastfed Chinese Infants: Renal Clearance, Body Burden, and Implications |
| Breast milk | 12.28 | ng/L | Human milk, China (n = 1,151); median | PDF p.6, Table 2, PFNA row, 50th column | Emerging and Legacy Perfluoroalkyl Substances in Breastfed Chinese Infants: Renal Clearance, Body Burden, and Implications |
| Breast milk | 50.37 | ng/L | Human milk, China (n = 1,151); 95th percentile | PDF p.6, Table 2, PFNA row, 95th column | Emerging and Legacy Perfluoroalkyl Substances in Breastfed Chinese Infants: Renal Clearance, Body Burden, and Implications |
| Breast milk | 307.0 | ng/L | Human milk, China (n = 1,151); maximum | PDF p.6, Table 2, PFNA row, Max column | Emerging and Legacy Perfluoroalkyl Substances in Breastfed Chinese Infants: Renal Clearance, Body Burden, and Implications |