Table 1.
Reference | Sampling Year |
Chemicals of Concern |
Targeted Population | Number of Samples |
Sampling Length |
Units of Measurement |
Location |
---|---|---|---|---|---|---|---|
| |||||||
Aerts et al., 2018 | 2016 | Pesticide Residues | NA | n = 30 participants, n = 30 participant residences, n = 4 participant workplace, n=8 forest | 5 days | ng/g WB | Belgium |
Alkon et al., 2021 | 2017–19 | Pesticides | Preschool age children | n = 125 | 30- weekday hours | ng/g WB | Northern California, USA |
Arcury et al., 2021 | 2018–19 | Pesticides | 8-year-old LatinX children | n = 60 urban non-farmworker families, n = 75 rural farmworker families | 7 days | Number of chemical detections/WB | North Carolina, USA |
Baum et al., 2020 | 2017 | PAHs | Structural firefighters | n = 72 | 24 hours | ng/g WB | Southern Florida, USA |
Bergmann et al., 2017 | 2014 | Pesticides and SVOCs | NA | n = 68 | 1 month | ng/g WB | Alto Mayo, Peru |
Bullock et al., 2020 | 2016 | VOCs and SVOCs | Beehives | n = 10 apiaries across 3 time points, and three locations within each apiary | 24 hours | Number of chemical detections/ WB | southeastern Pennsylvania, USA |
Caban-Martinez et al., 2020 | 2019 | PAHs | Structural firefighters | n = 15 | 24 hours | ng/g WB | Dominican Republic |
Craig et al., 2019 | 2016–17 | Phthalates, phthalate alternatives, OPEs | Nail Salon Workers (females, >18yo) | n = 9 wristbands and pinned lapels each | 1 work day | ng/g WB | Boston, Massachusetts, USA |
Dixon et al., 2018 | 2013–15 | PAHs | Pregnant women | n = 22 | 48 hours | ng/WB | New York, New York, USA |
Hendryx et al., 2020 | 2017–18 | PAHs | Appalachian coal mining communities with surface coal mining | n= 101 | 7 days | ng/g WB | Rural communities in the Central Appalachian portion of southern West Virginia, eastern Kentucky, and western Virginia |
Hoffman et al., 2021 | 2018–19 | OPEs | North Carolina adults | n= 10 (1 wristband per day) | 5 days | ng/g WB | North Carolina, USA |
Kile et al., 2016 | 2012–13 | PBDEs, OPEs, and HFRs | Preschool children (3–5yo) | n = 72 | 7 days | ng/g WB/day | Lane and Benton Counties, Oregon, USA |
Levasseur et al., 2021 | 2014–16 | Environmental phenols | Children aged 3–6 | n = 76 | 7 days | ng/g WB | central North Carolina, USA |
Dixon et al., 2019 | 2014–17 | VOCs and SVOCs | NA | n = 262 worn by 246 volunteers | Varied | Number of chemical detections/WB | Locations within Africa, North America, and South America |
Doherty et al., 2020 | 2017–18 | VOCs and SVOCs | Pregnant women | n = 255 at 12 gestational weeks, n = 20 at 24 gestational weeks | 7 days | ng/g WB | New Hampshire, USA |
Donald et al., 2016 | 2014 | Pesticides | Farmworkers | n = 35 for two time periods | 5 days | ng/g WB | Diender, Senegal |
Gibson et al., 2016 | -- | OPEs | Mother and Child (3–6 yo) pairs | n = 32 pairs for two consecutive periods | 7 days | ng/g WB | New York, New York, USA |
Hammel et al., 2016 | 2015 | OPEs | NA | n = 40 | 5 days | ng/WB | Durham, North Carolina, USA |
Hammel et al., 2018 | 2016 | HFRs | NA | n = 30 | 7 days | ng/g WB | Durham, North Carolina, USA |
Hammel et al., 2020 | 2015–16 | OPEs & phthalates | Children (3–6 yo) | n = 77 | 7 days | ng/g WB | North Carolina, USA |
Harley et al., 2019 | 2016 | Pesticides | Latina adolescent girls in a farm working community | n = 97 | 7 days | ng/g WB/day | Salinas Valley, California, USA |
Manzano et al., 2019 | 2016–17 | Targeted and untargeted SVOC analysis | Individuals in areas with different geographical/socioeconomic characteristics | n = 27; two time points (winter & summer) | 5 days | ng/g WB | Santiago, Chile |
Mendoza-Sanchez et al., 2021 | 2015–16 | PAHs | Pregnant women | n = 17 for three consecutive periods | 24 hours | ng/WB | McAllen, Texas, USA |
Nguyen et al., 2020 | 2017 | PBDEs & HFRs | e-waste recycling facility workers | n = 45 workers; n = 45 silicone brooches, n = 28 wristbands, and n = 9 armbands | 1 work day | ng/dm2 WB/h | Québec, Canada |
O’Connell et al., 2014 | 2012 | PAHs | Roofers using hot asphalt | Worksite 1 (n = 3), worksite 2 (n = 5). Single, stacked and lapel/brooch wristbands deployed to every participant | 8hrs and workweek (32–39 hrs) | ng/WB | Willamette Valley, Oregon, USA |
Paula Corrêa et al., 2021 | 2016–17 | VOCs & SVOCs | NA | n = 2 | 6 hours | ng/g WB | Brazilian cities |
Paulik et al., 2018 | 2014 | PAHs | Individuals in close proximity to natural gas extraction sites | n= 19 | 3 weeks | ng/g WB | Carroll County, Ohio, USA |
Poutasse et al., 2020 | 2018–19 | PAHs, VOCs & SVOCs | Structural Firefighters | nlow volume = 29; nhigh volume = 27 for on duty and off duty | 30 on-duty and off duty days | pmol/g tag | Kansas City, Kansas/Missouri, USA |
Poutasse et al., 2022 | 2018–19 | Potential Endocrine Disruptors | Structural Firefighters | nlow volume= 29; nhigh volume = 27 for on duty and off duty | 30 on-duty and off duty days | nmol/tag | Kansas City, Kansas/Missouri, USA |
Quintana et al., 2019 | 2017 | Nicotine | Children (4–14 yo) who lived with/without smoking adults | n= 31 children | 2 and 7 days | ng/WB | San Diego, California, USA |
Santiago et al., 2021 | 2018 | PAHs | Fishermen | n= 17 | 24 work hrs | ng/g WB | Mississippi & Florida, USA |
Swanson et al., 2018 | 2015–16 | Pesticides | Northern leopard frogs (Lithobates pipiens) | n = 72 | 2 weeks | ng/WB | northern Iowa, USA |
Travis et al., 2020 | 2018 | PCBs, pesticides, PBDE, OPEs, HFR | Elementary school children | n = 24 | 7 days | ng/g WB | Montevideo, Uruguay |
Quintana et al., 2021 | 2017–18 | Nicotine, cotinine, and tobacco-specific nitrosamines | Children (4–14 yo) who lived with/without smoking adults | n= 53 children, two wristbands were worn at the same time for 7 days, an additional wristband was worn the last two days | 2 and 7 days | ng/g WB | San Diego, California, USA |
Reche et al., 2020 | 2019 | PAHs and personal care products | Volunteers in close proximity to professional athletes | n = 5 | 4.4 days | ng/WB | Yokohama, Kanagawa, Japan |
Reddam et al., 2020 | 2019 | OPEs | University of California, Riverside students who commute | n = 89 | 5 days | ng/g WB | Riverside, California, USA |
Rohlman et al., 2019 | 2015 | PAHs | Individuals with moderate to severe asthma | n= 10 | 7 days | ng/WB | Eugene, Oregon, USA |
Rohlman et al., 2019 | 2016–17 | PAHs | Native American Communities | Spring (n = 10), Winter (n=22) | 7 days | ng/g WB | Swinomish Indian Tribal Community, Washington, USA |
Roodt et al., 2018 | NA | Skin VOCs and SVOCs | NA | Subject 1 (6 wristbands, and 6 anklet samples), subject 2 (2 wristbands during 2 separate sample collections). | 4 hours | Normalized mean peak area | Pretoria, South Africa |
Wang et al., 2019 | 2018 | PAHs, PBDE, HFRs, and OPEs | NA | n= 10 | 72 hours | ng/WB | Bloomington, Indiana, USA |
Wang et al., 2020 | 2018–19 | PAHs, PBDEs, HFRs, and OPEs | NA | France (n = 40) and Italy (n = 31) | 5 days | ng/g WB | Turin, Italy and France |
Wang et al., 2020 | 2018 | PBDEs, HFRs, OPEs, and dechlorane plus (DPs) | e-waste recycling facility workers | n= 15 | 24 hours | ng/WB/h | Dhaka, Bangladesh |
Wise et al., 2020 | 2018 | VOCs & SVOCs | Human dog pairs | n = 30 human and dog pairs | 5 days | ng/g WB | Wake County, North Carolina, and New Jersey, USA |
Wise et al., 2021 | 2018 | Pesticides | Human dog pairs | n = 30 human and dog pairs | 5 days | ng/g WB | Wake County, North Carolina, and New Jersey, USA |
Wooding et al., 2020 | NA | Skin VOCs and SVOCs | NA | n = 20 (replicates of three for each wristband & anklet sampler) sampled on 5 consecutive days | 1 hr | Normalized mean peak area | Pretoria, South Africa |
Xie et al., 2021 | 2018–19 | OPEs | Mother-child pairs | n = 47 mother- child pairs | 2 weeks | ng/WB | Guangzhou, South China |
Young et al., 2021 | 2019 | PCBs, PBDEs, HFRs, OPEs, phthalates & phthalate alternatives, pesticides, & PAHs | Adult workers in office buildings | n = 251 from 36 office buildings | Monday-Thursday during work hrs. | ng/g WB | USA, UK, China, & India |