| 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, PFDA 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) | 0.50 | µg/kg f.w. | Perch, Finnish rivers and coastal sites (n = 48), fresh weight; mean | PDF p.9, Table 5, PFDA row, Perch Mean column | PFASs in Finnish Rivers and Fish and the Loading of PFASs to the Baltic Sea |
| Fish, freshwater (tilapia, catfish, trout) | 1.6 | µg/kg f.w. | Perch, Finnish rivers and coastal sites (n = 48), fresh weight; maximum | PDF p.9, Table 5, PFDA row, Perch Max column | PFASs in Finnish Rivers and Fish and the Loading of PFASs to the Baltic Sea |
| Seafood | 0.07 ± 0.02 | ng/g | Fish cake, untreated control, Korea; mean ± SD | PDF p.5, Table 2, PFDA row, Control column | Reduction of perfluorinated compound content in fish cake and swimming crab by different cooking methods |
| Fish, freshwater (tilapia, catfish, trout) | 0.74 (0.07-2.39) | µg/kg | Coregonus wartmanni fillets, Switzerland 2022-2024 (N = 20); average (min-max) | PDF p.5, Table 1, PFDA 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) | 95% | µg/kg | Coregonus wartmanni fillets, Switzerland 2022-2024 (N = 20); frequency of positives above LOQ | PDF p.5, Table 1, PFDA 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) | 0.37 (0.09-1.52) | µg/kg | Cyprinus carpio fillets, Switzerland 2022-2024 (N = 11); average (min-max) | PDF p.5, Table 1, PFDA 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) | 100% | µg/kg | Cyprinus carpio fillets, Switzerland 2022-2024 (N = 11); frequency of positives above LOQ | PDF p.5, Table 1, PFDA 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) | 0.02 (0.01-0.04) | µg/kg | Oncorhynchus mykiss fillets, Switzerland 2022-2024 (N = 11); average (min-max) | PDF p.5, Table 1, PFDA 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) | 64% | µg/kg | Oncorhynchus mykiss fillets, Switzerland 2022-2024 (N = 11); frequency of positives above LOQ | PDF p.5, Table 1, PFDA 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) | 1.43 (0.04-4.60) | µg/kg | Perca fluviatilis fillets, Switzerland 2022-2024 (N = 38); average (min-max) | PDF p.5, Table 1, PFDA 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) | 79% | µg/kg | Perca fluviatilis fillets, Switzerland 2022-2024 (N = 38); frequency of positives above LOQ | PDF p.5, Table 1, PFDA row, Perca fluviatilis F (%) column | Determination of per- and polyfluoroalkyl substances (PFAS) in six different fish species from Swiss lakes |
| Fish, freshwater (tilapia, catfish, trout) | 0.50 (0.02-1.56) | µg/kg | Squalius cephalus fillets, Switzerland 2022-2024 (N = 7); average (min-max) | PDF p.5, Table 1, PFDA row, Squalius cephalus Av (min-max) column | Determination of per- and polyfluoroalkyl substances (PFAS) in six different fish species from Swiss lakes |
| Fish, freshwater (tilapia, catfish, trout) | 57% | µg/kg | Squalius cephalus fillets, Switzerland 2022-2024 (N = 7); frequency of positives above LOQ | PDF p.5, Table 1, PFDA row, Squalius cephalus F (%) column | Determination of per- and polyfluoroalkyl substances (PFAS) in six different fish species from Swiss lakes |
| Breast milk | 21 | pg/mL | Mother's milk, Shanghai (n = 10); average | PDF p.5, Table 1, L-PFDA row, Shanghai Conc. column | Emerging per- and polyfluoroalkyl substances (PFAS) in human milk from Sweden and China |
| Breast milk | <10-42 | pg/mL | Mother's milk, Shanghai (n = 10); range | PDF p.5, Table 1, L-PFDA row, Shanghai range in parentheses column | Emerging per- and polyfluoroalkyl substances (PFAS) in human milk from Sweden and China |
| Breast milk | 64 | pg/mL | Mother's milk, Jiaxing (n = 10); average | PDF p.5, Table 1, L-PFDA row, Jiaxing Conc. column | Emerging per- and polyfluoroalkyl substances (PFAS) in human milk from Sweden and China |
| Breast milk | 15-139 | pg/mL | Mother's milk, Jiaxing (n = 10); range | PDF p.5, Table 1, L-PFDA row, Jiaxing range in parentheses column | Emerging per- and polyfluoroalkyl substances (PFAS) in human milk from Sweden and China |
| Breast milk | 47 | pg/mL | Mother's milk, Shaoxing (n = 10); average | PDF p.5, Table 1, L-PFDA row, Shaoxing Conc. column | Emerging per- and polyfluoroalkyl substances (PFAS) in human milk from Sweden and China |
| Breast milk | <10-106 | pg/mL | Mother's milk, Shaoxing (n = 10); range | PDF p.5, Table 1, L-PFDA 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-PFDA row, Stockholm Conc. column | Emerging per- and polyfluoroalkyl substances (PFAS) in human milk from Sweden and China |
| Breast milk | <10-15 | pg/mL | Mother's milk, Stockholm (n = 10); range | PDF p.5, Table 1, L-PFDA 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 | ND | 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 |
| Cereal grains | 5.12 | ng/g w.w. | Rice, Taiwan market samples (n = 10); median | PDF p.5, Table 2, Rice row, PFDA row, PFDA median column | Concentrations of perfluoroalkyl substances in foods and the dietary exposure among Taiwan general population and pregnant women |
| Cereal grains | 2.21 | ng/g w.w. | Flour, Taiwan market samples (n = 10); median | PDF p.5, Table 2, Flour row, PFDA row, PFDA median column | Concentrations of perfluoroalkyl substances in foods and the dietary exposure among Taiwan general population and pregnant women |
| Meat and poultry | 3.63 | ng/g w.w. | Pork, Taiwan market samples (n = 10); median | PDF p.5, Table 2, Pork row, PFDA row, PFDA median column | Concentrations of perfluoroalkyl substances in foods and the dietary exposure among Taiwan general population and pregnant women |
| Meat and poultry | 3.70 | ng/g w.w. | Beef, Taiwan market samples (n = 10); median | PDF p.5, Table 2, Beef row, PFDA row, PFDA median column | Concentrations of perfluoroalkyl substances in foods and the dietary exposure among Taiwan general population and pregnant women |
| Meat and poultry | 3.35 | ng/g w.w. | Chicken, Taiwan market samples (n = 10); median | PDF p.5, Table 2, Chicken row, PFDA row, PFDA median column | Concentrations of perfluoroalkyl substances in foods and the dietary exposure among Taiwan general population and pregnant women |
| Meat and poultry | 26.5 | ng/g w.w. | Liver, Taiwan market samples (n = 10); median | PDF p.5, Table 2, Liver row, PFDA row, PFDA median column | Concentrations of perfluoroalkyl substances in foods and the dietary exposure among Taiwan general population and pregnant women |
| Seafood | 8.55 | ng/g w.w. | Salmon, Taiwan market samples (n = 10); median | PDF p.5, Table 2, Salmon row, PFDA row, PFDA median column | Concentrations of perfluoroalkyl substances in foods and the dietary exposure among Taiwan general population and pregnant women |
| Seafood | 10.5 | ng/g w.w. | Oyster, Taiwan market samples (n = 10); median | PDF p.5, Table 2, Oyster row, PFDA row, PFDA median column | Concentrations of perfluoroalkyl substances in foods and the dietary exposure among Taiwan general population and pregnant women |
| Seafood | 7.36 | ng/g w.w. | Shrimp, Taiwan market samples (n = 10); median | PDF p.5, Table 2, Shrimp row, PFDA row, PFDA median column | Concentrations of perfluoroalkyl substances in foods and the dietary exposure among Taiwan general population and pregnant women |
| Seafood | 7.05 | ng/g w.w. | Clam, Taiwan market samples (n = 10); median | PDF p.5, Table 2, Clam row, PFDA row, PFDA median column | Concentrations of perfluoroalkyl substances in foods and the dietary exposure among Taiwan general population and pregnant women |
| Seafood | 7.84 | ng/g w.w. | Squid, Taiwan market samples (n = 10); median | PDF p.5, Table 2, Squid row, PFDA row, PFDA median column | Concentrations of perfluoroalkyl substances in foods and the dietary exposure among Taiwan general population and pregnant women |
| Fish, freshwater (tilapia, catfish, trout) | 7.59 | ng/g w.w. | Grass Carp, Taiwan market samples (n = 10); median | PDF p.5, Table 2, Grass Carp row, PFDA row, PFDA median column | Concentrations of perfluoroalkyl substances in foods and the dietary exposure among Taiwan general population and pregnant women |
| Eggs | 23.1 | ng/g w.w. | Egg, Taiwan market samples (n = 10); median | PDF p.5, Table 2, Egg row, PFDA row, PFDA median column | Concentrations of perfluoroalkyl substances in foods and the dietary exposure among Taiwan general population and pregnant women |
| Liquid milk, cow | 1.53 | ng/mL | Milk, Taiwan market samples (n = 10); median | PDF p.5, Table 2, Milk row, PFDA row, PFDA median column | Concentrations of perfluoroalkyl substances in foods and the dietary exposure among Taiwan general population and pregnant women |
| Bottled drinking water (purified, spring, artesian) | 0.07 | 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 |
| Liquid milk, cow | N.D. | 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 | N.D. | 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 |
| Liquid milk, cow | N.D. | pg g−1 | Raw cow milk fraction Whole Milk; 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 | 0.10 | 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 | 0.06 | 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 | <0.03 | 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 | 0.22 (0.19, 0.94) | ng/L | median (IQR), detected archived tap-water samples only | PDF p3, Table 2, PFDA | 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 | 0.14 [0.03, 0.3] | 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 | 0.08 [0.03, 0.28] | 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 | 0.2 | ng/L | drinking-water application samples; content range or single reported value | PDF p12, 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 |
| Breast milk | n.d.-8.7 | ng/L | Breast milk, Austria, follow-up study 2014-2016 (n = 40); range | PDF p.11, Table 3, follow-up study block, PFDA row, follow-up range column | Persistent Organic Pollutants in Austrian Human Breast Milk Collected between 2013 and 2016 |
| Breast milk | n.d. | ng/L | Breast milk, Austria, follow-up study 2014-2016 (n = 40); median | PDF p.11, Table 3, follow-up study block, PFDA row, follow-up median column | Persistent Organic Pollutants in Austrian Human Breast Milk Collected between 2013 and 2016 |
| Breast milk | 4.6 | ng/L | Breast milk, Austria, follow-up study 2014-2016 (n = 40); 95th percentile | PDF p.11, Table 3, follow-up study block, PFDA 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, PFDA row, Cleaner column | Perfluoroalkyl and polyfluoroalkyl substances in consumer products |
| Textiles, apparel and outdoor gear | 100 | % | German consumer products, Outdoor samples (percentage with detected PFAS); percentage of samples detected | PDF p.7, Table 3, PFDA 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, PFDA row, Carpet column | Perfluoroalkyl and polyfluoroalkyl substances in consumer products |
| Bottled drinking water (purified, spring, artesian) | 0.5 | 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 | 0.0021 | 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 | 0.0021 | 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-0.0021 | 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 | <LOQ | 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 |
| Children's products | 89 | µg/m² | Stuffed toys, PFAS migration (not total content); detection frequency (%) | PDF p.5, Table 1, PFDA row, DF (%) column | Stuffed toys as a source of oral PFAS exposure: Migration into artificial saliva and exposure assessment |
| Children's products | 0.07 | µg/m² | Stuffed toys, PFAS migration (not total content); mean migration (as reported) | PDF p.5, Table 1, PFDA 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 - 0.10 | µg/m² | Stuffed toys, PFAS migration (not total content); range of migration | PDF p.5, Table 1, PFDA row, Range [μg/m²] column | Stuffed toys as a source of oral PFAS exposure: Migration into artificial saliva and exposure assessment |
| Infant Formula | 5/20 (25) | count (%) | Infant formula; Frequency | PDF p.9 Table 1 | Study of Endocrine-Disrupting Chemicals in Infant Formulas and Baby Bottles: Data from the European LIFE-MILCH PROJECT |
| Infant Formula | 0.01 ± 0.001 | ng/g dry weight | Infant formula; Mean ± SD | PDF p.9 Table 1 | Study of Endocrine-Disrupting Chemicals in Infant Formulas and Baby Bottles: Data from the European LIFE-MILCH PROJECT |
| Infant Formula | 0.01 | ng/g dry weight | Infant formula; Median | PDF p.9 Table 1 | Study of Endocrine-Disrupting Chemicals in Infant Formulas and Baby Bottles: Data from the European LIFE-MILCH PROJECT |
| Infant Formula | 0.009-0.011 | ng/g dry weight | Infant formula; Min-Max | PDF p.9 Table 1 | Study of Endocrine-Disrupting Chemicals in Infant Formulas and Baby Bottles: Data from the European LIFE-MILCH PROJECT |
| Children's products | 4.9% (3/61) | % | Children's and bedding textile products, US (n = 61, targeted analysis); detection frequency (detected/analyzed) | PDF p.5, Table 3, PFDA 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 | 11.8 | ng/g | same; maximum | PDF p.5, Table 3, PFDA 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 | 0.108 | ng/cm2 | same; maximum | PDF p.5, Table 3, PFDA 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) | 0.07 | 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 | 24.0 | ng/g | Children's products, China, School uniform (n = 25); detection frequency (%) | PDF p.5, Table 1, PFDA row, School uniform DF column | Per- and Polyfluoroalkyl Substances in North American School Uniforms |
| Textiles, apparel and outdoor gear | ND-0.397 | ng/g | Children's products, China, School uniform (n = 25); range | PDF p.5, Table 1, PFDA row, School uniform Range column | Per- and Polyfluoroalkyl Substances in North American School Uniforms |
| Textiles, apparel and outdoor gear | 87.5 | ng/g | Children's products, China, Outdoor wear (n = 16); detection frequency (%) | PDF p.5, Table 1, PFDA row, Outdoor wear DF column | Per- and Polyfluoroalkyl Substances in North American School Uniforms |
| Textiles, apparel and outdoor gear | 0.277 | ng/g | Children's products, China, Outdoor wear (n = 16); median (non-detects set to 1/2 MDL) | PDF p.5, Table 1, PFDA row, Outdoor wear Median column | Per- and Polyfluoroalkyl Substances in North American School Uniforms |
| Textiles, apparel and outdoor gear | ND-1.79 | ng/g | Children's products, China, Outdoor wear (n = 16); range | PDF p.5, Table 1, PFDA row, Outdoor wear Range column | Per- and Polyfluoroalkyl Substances in North American School Uniforms |
| Children's products | 43.8 | ng/g | Children's products, China, Miscellaneous (n = 16); detection frequency (%) | PDF p.5, Table 1, PFDA row, Miscellaneous DF column | Per- and Polyfluoroalkyl Substances in North American School Uniforms |
| Children's products | ND-0.967 | ng/g | Children's products, China, Miscellaneous (n = 16); range | PDF p.5, Table 1, PFDA row, Miscellaneous Range column | Per- and Polyfluoroalkyl Substances in North American School Uniforms |
| Breast milk | 99.2 | ng/L | Human milk, China (n = 1,151); detection rate (%) | PDF p.6, Table 2, PFDA row, DR (%) column | Emerging and Legacy Perfluoroalkyl Substances in Breastfed Chinese Infants: Renal Clearance, Body Burden, and Implications |
| Breast milk | <LOQ | ng/L | Human milk, China (n = 1,151); minimum | PDF p.6, Table 2, PFDA row, Min column | Emerging and Legacy Perfluoroalkyl Substances in Breastfed Chinese Infants: Renal Clearance, Body Burden, and Implications |
| Breast milk | 8.721 | ng/L | Human milk, China (n = 1,151); median | PDF p.6, Table 2, PFDA row, 50th column | Emerging and Legacy Perfluoroalkyl Substances in Breastfed Chinese Infants: Renal Clearance, Body Burden, and Implications |
| Breast milk | 59.24 | ng/L | Human milk, China (n = 1,151); 95th percentile | PDF p.6, Table 2, PFDA row, 95th column | Emerging and Legacy Perfluoroalkyl Substances in Breastfed Chinese Infants: Renal Clearance, Body Burden, and Implications |
| Breast milk | 798.3 | ng/L | Human milk, China (n = 1,151); maximum | PDF p.6, Table 2, PFDA row, Max column | Emerging and Legacy Perfluoroalkyl Substances in Breastfed Chinese Infants: Renal Clearance, Body Burden, and Implications |