Previous Chapter: Appendix B: UV Filter Usage
Suggested Citation: "Appendix C: UV Filter Water and Sediment Occurrence Data." National Academies of Sciences, Engineering, and Medicine. 2022. Review of Fate, Exposure, and Effects of Sunscreens in Aquatic Environments and Implications for Sunscreen Usage and Human Health. Washington, DC: The National Academies Press. doi: 10.17226/26381.
Suggested Citation: "Appendix C: UV Filter Water and Sediment Occurrence Data." National Academies of Sciences, Engineering, and Medicine. 2022. Review of Fate, Exposure, and Effects of Sunscreens in Aquatic Environments and Implications for Sunscreen Usage and Human Health. Washington, DC: The National Academies Press. doi: 10.17226/26381.

TABLE C.1 Reported Concentrations of UV Filters in Water (ng/l for organic and μg/L for inorganic)

Citation Location Oxybenzone Sulisobenzone Homosalate Octocrylene Octisalate
Bargar et al., 2015 Trunk Bay, USVI 6,073 1,413 ND
Bargar et al., 2015 Hawksnest Bay, USVI > 1,000; < 10,000 > 100; < 1,000 ND
Downs et al., 2021 Hanauma Bay, HI 30–27,880 with 40% > 1,000
Tsui et al., 2014b Hong Kong Harbor 39–5,429 54–389 66–2,812 103–6,812 61–1,030
Bratkovics et al., 2015 Fishing Pier at Folly Beach area, SC 39–5,429 ND ND–3,730; summer average = 2,016
Díaz-Cruz et al., 2019 Evrotas River (Greece) < 0.2–2,031 ND
Bratkovics and Sapozhnikova, 2011 Wash Out Beach at Folly Beach, SC ND–1,766; summer average = 787 ND ND–1,375; summer average = 745
Downs et al., 2016 Trunk Bay, USVI 580,000–1,395,000
Kung et al., 2018 Wanlitong Beach, Taiwan; 1 summer sampling event 1,233
Schaap and Slijkerman, 2018 Sorobon, Bonaire August 2018 1,540 810
Tashiro and Kameda, 2013 Tropical Beach, Okinawa, Japan 2.2–1,258 0.8–214 0.5–50 ND–2.1
Bratkovics et al., 2015 County Park and beach on Folly Island, SC ND–2,126; summer average = 1,264 ND ND–1,060; summer average = 878
Tarazona et al., 2010 3 beaches on Mediterranean coast of Spain in summer 1,340–3,300
Downs et al., 2016 Hawknest Bay, USVI 75,000–95,000
Sánchez Rodríguez et al., 2015 Beaches in the Canary Islands over 1 year at beach AM 91.0 (median); 12.7–2,675.7 4.85; < 1.3–163.5 24.3; < 2.4–319.0 160.4 (median); 30.7–766.7
Sánchez Rodríguez et al., 2015 Beaches in the Canary Islands over 1 year at beach MG 343.2 (median); 54.2–3,316.7 29.6 (median); < 4.2–144.4 151.7 (median); 10.8–526.1 497.8 (median); 37.8–1,324.9
Bargar et al., 2015 Cinnamon Bay, USVI > 100; < 1,000 ND–100 ND
Bargar et al., 2015 Maho Bay, USVI > 100; < 1,000 > 10–< 100 ND
Suggested Citation: "Appendix C: UV Filter Water and Sediment Occurrence Data." National Academies of Sciences, Engineering, and Medicine. 2022. Review of Fate, Exposure, and Effects of Sunscreens in Aquatic Environments and Implications for Sunscreen Usage and Human Health. Washington, DC: The National Academies Press. doi: 10.17226/26381.
Octinoxate Avobenzone Dioxybenzone Ensulizole Padimate O Reported as Total Organic Titanium Dioxide (µg/L) Zinc Oxide(µg/L)
41 ND
> 10; < 100 ND
89–4,043 24–721 64–117 95–182
ND–438; summer average = 166 ND–1,298; summer average = 597 ND ND–191; summer average = 110 0.5–7,806
ND up to 25.1
ND–172; summer average = 108 ND–366; summer average = 235 ND ND–1.55; summer average = ND Maximum = 3,634; average = 530
ND
ND–32 ND–154; summer average = 44 ND–303; summer average = 173 ND ND ND Maximum = 3,093; average = 160
ND
10.5 (median); < 1.6–276.8 65.5 (median); < 6.7–792.0
57.2 (median); < 5.2–260.2 422.6 (median); 19.8–1770.3
~10 ND
ND–~10 ND
Suggested Citation: "Appendix C: UV Filter Water and Sediment Occurrence Data." National Academies of Sciences, Engineering, and Medicine. 2022. Review of Fate, Exposure, and Effects of Sunscreens in Aquatic Environments and Implications for Sunscreen Usage and Human Health. Washington, DC: The National Academies Press. doi: 10.17226/26381.
Citation Location Oxybenzone Sulisobenzone Homosalate Octocrylene Octisalate
Lee Blaney, 2021 Presentation to Committee Chester River, Chesapeake Bay, MD ~50–~125 ~10–~25 ~25–~50
Lee Blaney, 2021 Presentation to Committee Lower Eastern Shore, Chesapeake Bay, MD ~50–~150 ~100–~200 ~10–~50
Horricks et al., 2019 Grand Anse Beach, Grenda 123
Kung et al., 2018 Houwan Beach, Taiwan; 1 summer sampling event 566
Kung et al., 2018 Houbiu Beach, Taiwan; 1 summer sampling event 118
Kung et al., 2018 South Bay, Taiwan; 1 summer sampling event 230
Kung et al., 2018 Small Bay, Taiwan; 1 summer sampling event 216
Langford and Thomas, 2008 Sandvika Beach, Baerum, Norway in July at 3 locations 13.4–439.9 65.3–7,301
Langford and Thomas, 2008 Huk Beach, near Oslo Norway 5.4–32.1 ND–63.2
O’Malley et al., 2021 Enogerra Reservoir, Australia based on bar charts and reported values ~200–~700 ND (not commonly used in Australia) 1,380–4,660 Present at low levels
Tsui et al., 2014b New York City including Jamaica Bay, Upper New York Bay, and East River near WWTP discharges 23–178 89–574 91–114 117–128 ND
Tsui et al., 2014b Los Angeles at Huntington Beach 227–601 ND 142–270 145–377 53–120
Tsui et al., 2014b Shantou, China at beach 55–188 ND ND 75–107 ND
Tsui et al., 2014b Chao Phraya River at Bangkok, Thailand 86–116 89–95 29–59 153–205 28–56
Li et al., 2018 Popular beaches along coastline of Shenzhen, China ND–172
Suggested Citation: "Appendix C: UV Filter Water and Sediment Occurrence Data." National Academies of Sciences, Engineering, and Medicine. 2022. Review of Fate, Exposure, and Effects of Sunscreens in Aquatic Environments and Implications for Sunscreen Usage and Human Health. Washington, DC: The National Academies Press. doi: 10.17226/26381.
Octinoxate Avobenzone Dioxybenzone Ensulizole Padimate O Reported as Total Organic Titanium Dioxide (µg/L) Zinc Oxide(µg/L)
ND–~150
~10–~25
ND ND
ND
ND
ND
ND
60.4–389.9
38.6–159.2
Present at low levels 424–1,130 Present at low levels 2,550–7,330
89–150 70–87 72–92 ND
91–138 67–109 29–96 ND
52–78 53–100 ND ND
88–95 36–38 63–71 ND
ND–89 ND–69 ND–10.1 ND–644
Suggested Citation: "Appendix C: UV Filter Water and Sediment Occurrence Data." National Academies of Sciences, Engineering, and Medicine. 2022. Review of Fate, Exposure, and Effects of Sunscreens in Aquatic Environments and Implications for Sunscreen Usage and Human Health. Washington, DC: The National Academies Press. doi: 10.17226/26381.
Citation Location Oxybenzone Sulisobenzone Homosalate Octocrylene Octisalate
Sánchez Rodríguez et al., 2015 Beaches in the Canary Islands over 1 year at beach PR 238.7 (median); 32.8–979.8 14.7 (median); < 4.2–228.7 60.6 (median); 9.2–536.2 374.5 (median); 61.2–973.1
Tashiro and Kameda, 2013 Emerald Beach, Okinawa, Japan ND–141 ND–34 0.2–78 ND–10
Tashiro and Kameda, 2013 Sunset Beach, Okinawa, Japan 10–448 0.6–87 0.5–27 ND–3.3
Tashiro and Kameda, 2013 Araha Beach, Okinawa, Japan 0.5–428 0.6–67 2.3–79 ND–2.1
Grabicova et al., 2013 Recreational ponds in Czech Republic 21–550 4–46
Tovar-Sánchez, 2013 Popular beaches on Majorca Island, Spain, sampled 2 days in August 76–155 with max at 1 beach of 400 at midday to afternoon
Bratkovics et al., 2015 Coast Guard Stations Estuarine Research Reserve, SC ND–467: summer average = 2332 ND–311; summer average = 162
Nguyen et al., 2011 3 locations along the Ligurion coast (Italy) sampled monthly June –August 2010 ND–118
He et al., 2019a Manokin River, Chesapeake Bay, MD 52.7–113.7 71.9–187.9 24.5–43.7
Mitchelmore et al., 2019 Waikiki Beach Hawaii Nearshore 8.8–142.7 93.7–686.6 0.3–29.1 39.1–66
Mitchelmore et al., 2019 Waikiki Beach Hawaii–offshore 9.4–73.1 107.3–192.0 2.7–8.6 43.1–79.1
Bratkovics et al., 2015 Myrtle Beach, SC ND–575; summer average = 329 ND ND–382; summer average = 261
Bratkovics et al., 2015 North Inlet National Estuarine Research Reserve, SC ND–138; summer average = 34 ND ND–77; summer average = 26
Sánchez Rodríguez et al., 2015 Beaches in the Canary Islands over 1 year at beach AL 3.7 (median); < 1.4–158.0 < 1.3 (median); < 1.3–34.7 < 2.4(median); < 2.4–84.8 20.9 (median); < 2.8–183.2
Sánchez Rodríguez et al., 2015 Beaches in the Canary Islands over 1 year at beach CA 9.6 (median); < 1.4–182.6 < 1.3 (median); < 1.3–176.3 < 2.4 (median); < 2.4–102.2 52.7 (median); < 2.8–768.5
Gago-Ferrero et al., 2013 Llobregat River, NE Spain for 5 samples in 2011 ND–37.8 30.4–862
Suggested Citation: "Appendix C: UV Filter Water and Sediment Occurrence Data." National Academies of Sciences, Engineering, and Medicine. 2022. Review of Fate, Exposure, and Effects of Sunscreens in Aquatic Environments and Implications for Sunscreen Usage and Human Health. Washington, DC: The National Academies Press. doi: 10.17226/26381.
Octinoxate Avobenzone Dioxybenzone Ensulizole Padimate O Reported as Total Organic Titanium Dioxide (µg/L) Zinc Oxide(µg/L)
71.0 (median); < 1.6–756.4 307.5 (median); 35.6–1,163.2
ND–143 ND–0.6
0.1–14 ND–0.8
ND–25 ND
24–930
ND 1 (but higher in surface micro-layer)
ND–235; summer average = 37 ND–138; summer average = 69 ND ND–28; summer average = 9 Maximum = 744; average = 192
ND–83
21.0–28.9
ND–1.5 ND 0.1–4.5 184.8–791.5
ND ND 2–12.4 187.6–298.6
ND–35; summer average = 12 ND–425; summer average = 160 ND ND–104; summer average is 35 Maximum = 1,287; average = 327
ND–140; summer average = 55 ND–158; summer average = 71 ND ND–77; summer average = 28 Maximum = 554; average = 118
< 5.2 (median); < 1.6–65.4 < 6.7 (median); < 2.0–314.3
7.3 (median); < 1.6–109.9 23.5 (median); < 2.0–737.1
Suggested Citation: "Appendix C: UV Filter Water and Sediment Occurrence Data." National Academies of Sciences, Engineering, and Medicine. 2022. Review of Fate, Exposure, and Effects of Sunscreens in Aquatic Environments and Implications for Sunscreen Usage and Human Health. Washington, DC: The National Academies Press. doi: 10.17226/26381.
Citation Location Oxybenzone Sulisobenzone Homosalate Octocrylene Octisalate
Pedrouzo et al., 2010 3 rivers in Catalonia, Spain; part of methods development 6–28 ND
Wick et al., 2010 sampling in 2 streams located downstream from the last discharge of a WWTP in September; streams are tributaries to the Main River in Germany ND–47 332–1,980
Balmer et al., 2005 Lake Greifensee, Switzerland surface 20–30 surface < 2–5
Balmer et al., 2005 Lake Hüttnersee, Switzerland surface 23–35 < 2
Tsui et al., 2014b Tokyo Bay 24–86 71–136 65–110 87–108 71–95
Langford and Thomas, 2008 Near offshore WWTP outfall (VEAS) from city of Oslo, Norway, July ND–15.5 ND–31.2
Langford and Thomas, 2008 Open waters of fjord off Baerum and Oslo, Norway, July 5.4–32.1 ND–63.2
Li et al., 2018 Less popular or undeveloped beaches along the Shenzhen, China coastline ND–28.7
Bargar et al., 2015 Leinster Bay, USVI ND–< 100 ND–< 100 ND
Bargar et al., 2015 Brown Bay, USVI 1.6–133 53–633.5 ND
Bargar et al., 2015 Great Lameshure Bay, USVI ND–< 100 ND–< 100 ND
da Silva et al., 2015 Tieta River at Jau Brazil (river water intake) 6 months of sampling ND–24 ND–208 ND
Downs et al., 2016 Maunalua Bay, Oahu, HI > 100–19,200
Suggested Citation: "Appendix C: UV Filter Water and Sediment Occurrence Data." National Academies of Sciences, Engineering, and Medicine. 2022. Review of Fate, Exposure, and Effects of Sunscreens in Aquatic Environments and Implications for Sunscreen Usage and Human Health. Washington, DC: The National Academies Press. doi: 10.17226/26381.
Octinoxate Avobenzone Dioxybenzone Ensulizole Padimate O Reported as Total Organic Titanium Dioxide (µg/L) Zinc Oxide(µg/L)
ND
1,310–3,240
Surface < 2
surface 3–5
46–95 78–104 76–96 ND
164.1–189.3
38.6–159.2
ND–53 ND–49 ND–7.6 ND–67
ND–~10 ND
15–20 ND
> 10; < 100 ND
ND–755
Suggested Citation: "Appendix C: UV Filter Water and Sediment Occurrence Data." National Academies of Sciences, Engineering, and Medicine. 2022. Review of Fate, Exposure, and Effects of Sunscreens in Aquatic Environments and Implications for Sunscreen Usage and Human Health. Washington, DC: The National Academies Press. doi: 10.17226/26381.
Citation Location Oxybenzone Sulisobenzone Homosalate Octocrylene Octisalate
Ekpeghere et al., 2016 Rivers in South Korea determined from box plots. Rivers include Nakdong River (9 sites), Guemho River (1 site) and Nam River (1 site) ~5–~50 ~30–~150
Tsui et al., 2014b Chaozhou, China at beach 37–49 ND–49 ND 36–102 121–128
Tsui et al., 2014b Arctic Ocean and Chukchi Sea 17–33 ND ND 26–31 ND
Fent et al., 2010 River Glatt below a WWTP, Switzerland 56 and 68
He et al., 2019a Chester River, Chesapeake Bay, MD 52–96 15.5–22.2 21.6–42.4
Emnet et al., 2015 Erubus Bay near a research station, Antarctica 2.6–88.4
He et al., 2019a Holland Straights, Chesapeake Bay,MD 40.4–59.3 78.4–99.8 11.9–20.6
He et al., 2019a Kitts Creek, Chesapeake Bay,MD 31.1–32 78.4–91.3 12.0–13.3
Kung et al., 2018 Boli River Estuary, Taiwan; 1 summer sampling event 41.4
Kung et al., 2018 Scichong River Estuary, Taiwan; 1 summer sampling event 45.4
Kung et al., 2018 Baisha Beach, Taiwan; 1 summer sampling event 23
Kung et al., 2018 Big Bay, Taiwan; 1 summer sampling event 18.8
Labille et al., 2020b 3 beaches along French Mediterranean in the bathing area (over 1 day) < 1–78 < 5–420
Suggested Citation: "Appendix C: UV Filter Water and Sediment Occurrence Data." National Academies of Sciences, Engineering, and Medicine. 2022. Review of Fate, Exposure, and Effects of Sunscreens in Aquatic Environments and Implications for Sunscreen Usage and Human Health. Washington, DC: The National Academies Press. doi: 10.17226/26381.
Octinoxate Avobenzone Dioxybenzone Ensulizole Padimate O Reported as Total Organic Titanium Dioxide (µg/L) Zinc Oxide(µg/L)
~20–~250
ND–79 ND ND
25–66 18–70 2–3.3
6
ND–115.0
12.0–21.4
7.6–18.6
ND
ND
ND
ND
< 5–8.8 < 5–309 < 8 3.6–541 ND–11.9
Suggested Citation: "Appendix C: UV Filter Water and Sediment Occurrence Data." National Academies of Sciences, Engineering, and Medicine. 2022. Review of Fate, Exposure, and Effects of Sunscreens in Aquatic Environments and Implications for Sunscreen Usage and Human Health. Washington, DC: The National Academies Press. doi: 10.17226/26381.
Citation Location Oxybenzone Sulisobenzone Homosalate Octocrylene Octisalate
Labille et al., 2020b 3 beaches along French Mediterranean beyond bathing area (over 1 day) < 1–26.7 < 5–141.6
Dominguez-Morueco et al., 2021 Northern Atlantic Peninsula ND–59
Kasprzyk-Hordern et al., 2008a,b River Taff (South Wales) in segment above and below wastewater discharges, 4 locations reported, based on several months of sampling from Nov 2006 to Aug 2007 ND–44 ND–371
Kameda et al., 2011 Rivers (18) and streams (2) in Japan considered polluted to varying degrees with domestic sewage and other pollutants sampled in August and September 2008 ND–41 ND–29 ND–9 ND–38
Tovar-Sanchez, 2013 Undeveloped coastal location on Majorca Island, Spain–1 day in September 36
Wu et al., 2013 2 rivers in northern Taiwan that receive direct discharges of municipal wastewater 12.3–15.4 ND ND–10.6
Rodil et al., 2008a 2 recreational lakes around Leipzig Germany in June 2007 27–55 ND–4 126–250 51
Rodil et al., 2008a 2 rivers around Leipzig Germany in May 2007 ND–30 ND–5 ND–16 ND
Tsui et al., 2017 Ung Kong, Hong Kong for wet and dry seasons 25.8 (wet); 29.1 (dry) 13.1 (wet); ND (dry)
Suggested Citation: "Appendix C: UV Filter Water and Sediment Occurrence Data." National Academies of Sciences, Engineering, and Medicine. 2022. Review of Fate, Exposure, and Effects of Sunscreens in Aquatic Environments and Implications for Sunscreen Usage and Human Health. Washington, DC: The National Academies Press. doi: 10.17226/26381.
Octinoxate Avobenzone Dioxybenzone Ensulizole Padimate O Reported as Total Organic Titanium Dioxide (µg/L) Zinc Oxide(µg/L)
< 5 < 5–48.1 < 8 4.7–5.9 ND–3.7
ND–1,040 ND–2
ND
20–33 2–5
ND–21 ND–3
ND ND
Suggested Citation: "Appendix C: UV Filter Water and Sediment Occurrence Data." National Academies of Sciences, Engineering, and Medicine. 2022. Review of Fate, Exposure, and Effects of Sunscreens in Aquatic Environments and Implications for Sunscreen Usage and Human Health. Washington, DC: The National Academies Press. doi: 10.17226/26381.
Citation Location Oxybenzone Sulisobenzone Homosalate Octocrylene Octisalate
Tsui et al., 2017 Sharp Island, Hong Kong for wet and dry seasons 24.4 (wet); 31.7 (dry) 9.7 (wet); ND (dry)
Tsui et al., 2017 Wu Pai, Hong Kong for wet and dry seasons 13.9 (wet); 13.8 (dry) 11.9 (wet); ND (dry)
Tsui et al., 2017 Sung Kong, Hong Kong for wet and dry seasons 13.2 (wet) 8.9 (wet); ND (dry)
Grabicova et al., 2013 Rivers with pollution in Czech Republic 16–67 4.6–390
da Silva et al., 2015 Araraquara or Tietje Rivers at Araraquara, Brazil (river water intake) monthly sampling over 1 year ND–38 ND ND
da Silva et al., 2015 Tiete River at Bauru (river water intake) 6 months sampling ND–28 ND–188 ND
da Silva et al., 2015 Feij≥o River at S≥o Carlos Brazil (river water intake) 6 months of sampling ND–44 ND ND
Mitchelmore et al., 2019 Kaneohe Bay Hawaii Shallow 4.7–11.3 ND ND–2.9 ND
Mitchelmore et al., 2019 Kaneohe Bay Hawaii Deep 0.1–48.1 ND–457.6 0.3–45.5 ND
Sánchez Rodríguez et al., 2015 Beaches in the Canary Islands over1 year at beach MP 4.6 (median); < 1.4–27.1 < 1.3 (median); < 1.3–< 4.2 < 2.4 (median); < 2.4–51.5 23.8 (median); < 9.3–359.1
Tsui et al., 2019 Coastal Hong Kong and adjacent South China Sea (concentrations decrease with distance seaward) 2.2–36.7 2.9–27.8 3.6–41.8 2.2–71.9 0.8–27.8
Fisch et al., 2017 Rivers draining to Baltic and coastline, Germany ND–11.4 ND ND–30.8
Suggested Citation: "Appendix C: UV Filter Water and Sediment Occurrence Data." National Academies of Sciences, Engineering, and Medicine. 2022. Review of Fate, Exposure, and Effects of Sunscreens in Aquatic Environments and Implications for Sunscreen Usage and Human Health. Washington, DC: The National Academies Press. doi: 10.17226/26381.
Octinoxate Avobenzone Dioxybenzone Ensulizole Padimate O Reported as Total Organic Titanium Dioxide (µg/L) Zinc Oxide(µg/L)
ND ND
ND ND
ND ND
11–500
ND–65
ND–669
ND–101
ND ND 0.1–3.9 6.4–15.4
ND ND 0.1–9.1 6.2–467.6
< 1.6 (median); < 1.6–16.1 < 6.7 (median); < 2.0–188.4
3.8–55.6 ND
ND
Suggested Citation: "Appendix C: UV Filter Water and Sediment Occurrence Data." National Academies of Sciences, Engineering, and Medicine. 2022. Review of Fate, Exposure, and Effects of Sunscreens in Aquatic Environments and Implications for Sunscreen Usage and Human Health. Washington, DC: The National Academies Press. doi: 10.17226/26381.
Citation Location Oxybenzone Sulisobenzone Homosalate Octocrylene Octisalate
Kasprzyk-Hordern et al., 2008b River Ely (South Wales, UK) in segment above and below wastewater discharges, 4 locations reported, based on several months of sampling from Nov 2006 to Aug 2007 ND ND–323
Balmer et al., 2005 Lake Zürichsee, Switzerland surface 10–20; deep (20 m) 10–11 surface < 2–~3; deep (20 m) < 2
Balmer et al., 2005 Lake Jörisee, Switzerland < 2 < 2
Allinson et al., 2018 Three estuaries flowing into Port Philp Bay, around Melbourne, Australia (4 water grab samples) in August 2011 (winter) 4.3–7.1 2–109 ND–31.6
Bargar et al., 2015 Trunk Bay, USVI at 210 m from shoreline 2.7 116.3 ND
Wick et al., 2010 Rhine River in Koblenz, Germany, in March 2008 ND 51
Downs et al., 2016 Caneel Bay, USVI ND
Downs et al., 2016 Kapalua Bay, Maui, HI ND
Downs et al., 2016 Kahekili Beach, Maui, HI ND
Horricks et al., 2019 Grand Anse Bay, Grenada deep 7
Horricks et al., 2019 Grand Mal, Grenada surface 7
Horricks et al., 2019 Grand Mal, Grenada deep ND
Horricks et al., 2019 True Blue, Grenada surface ND
Horricks et al., 2019 Quarantine Reef, Grenada surface ND
Horricks et al., 2019 Quarantine Reef, Grenada deep ND
Suggested Citation: "Appendix C: UV Filter Water and Sediment Occurrence Data." National Academies of Sciences, Engineering, and Medicine. 2022. Review of Fate, Exposure, and Effects of Sunscreens in Aquatic Environments and Implications for Sunscreen Usage and Human Health. Washington, DC: The National Academies Press. doi: 10.17226/26381.
Octinoxate Avobenzone Dioxybenzone Ensulizole Padimate O Reported as Total Organic Titanium Dioxide (µg/L) Zinc Oxide(µg/L)
surface < 2–7; deep (20 m) < 2
< 2
8.9–640 ND–0.4
5.8 ND
48
ND ND
ND
8 ND
ND ND
ND ND
ND ND
Suggested Citation: "Appendix C: UV Filter Water and Sediment Occurrence Data." National Academies of Sciences, Engineering, and Medicine. 2022. Review of Fate, Exposure, and Effects of Sunscreens in Aquatic Environments and Implications for Sunscreen Usage and Human Health. Washington, DC: The National Academies Press. doi: 10.17226/26381.
Citation Location Oxybenzone Sulisobenzone Homosalate Octocrylene Octisalate
Mitchelmore et al., 2019 Ka’a’awa Bay, Hawaii–nearshore 2.6–7.1 38.5–119.0 0.3–25.4 46–121.2
Mitchelmore et al., 2019 Ka’a’awa Bay, Hawaii–offshore 0.1–7.5 120.7–456.4 0.3–4.2 27.5–60.4
Fagervold et al., 2019 Villeneuve de la Raho Lake, France < 5
Schaap and Slijkerman, 2018 Sorobon, Bonaire November, 2018 < 10 160
Schaap and Slijkerman, 2018 Mangrove Lac Bay, Bonaire during August 10 < 20
Schaap and Slijkerman, 2018 Cai Reef, Bonaire < 10 < 20
Li et al., 2018 Drinking water reservoir in Shenzhen, China 9.2
Tashiro and Kameda, 2013 Shirahi River, Okinawa, Japan ND–9 ND–0.8 ND–2.5 ND–1.8
Tashiro and Kameda, 2013 CR coral reef site 660 m from Araha Beach, Okinawa, Japan ND–0.4 ND ND–8.1 ND–0.6
Tashiro and Kameda, 2013 BR Reef Site, 520 m from Emerald Bay, Okinawa, Japan ND–3.8 ND–3.2 ND–0.5 ND–0.1
Rodil et al., 2012 6 locations along Mero River in Galicia Spain, samples were collected on several occasions from November 2007 to September 2008 ND ND–603
Barbosa et al., 2018 Ave River, Portugal
Barbosa et al., 2018 Antua River, Portugal
Barbosa et al., 2018 Certima River, Portugal
Barbosa et al., 2018 Leca River, Portugal
Gondikas et al., 2014 Old Danube Recreational Lake, Vienna, Austria
Suggested Citation: "Appendix C: UV Filter Water and Sediment Occurrence Data." National Academies of Sciences, Engineering, and Medicine. 2022. Review of Fate, Exposure, and Effects of Sunscreens in Aquatic Environments and Implications for Sunscreen Usage and Human Health. Washington, DC: The National Academies Press. doi: 10.17226/26381.
Octinoxate Avobenzone Dioxybenzone Ensulizole Padimate O Reported as Total Organic Titanium Dioxide (µg/L) Zinc Oxide(µg/L)
ND ND ND–0.1 108.8–251.1
ND–1.5 ND 0.1–7.8 166.9–534.5
14.5 (average for July and August)
ND 29.59 ND 161
ND–3.9 ND
ND–1.5 ND
ND–2.3 ND
< 10–< 100
ND–168
ND–~225
ND–562
ND–~125
~1–~4 with Ti/Al ratios indicating elevated Ti during the bathing season
Suggested Citation: "Appendix C: UV Filter Water and Sediment Occurrence Data." National Academies of Sciences, Engineering, and Medicine. 2022. Review of Fate, Exposure, and Effects of Sunscreens in Aquatic Environments and Implications for Sunscreen Usage and Human Health. Washington, DC: The National Academies Press. doi: 10.17226/26381.
Citation Location Oxybenzone Sulisobenzone Homosalate Octocrylene Octisalate
Woodley (unpublished data) Near-shore waters Buck Island and Salt River Bay, St.Croix, U.S. Virgin Islands
Woodley (unpublished data) Popular snorkeling reefs in the Florida Keys during a time of low visitation
Picot-Groz et al., 2018 3 shoreline/beach sites along Gulf of Lion–1 day in July at beginning of tourist season ND–369 and illustrates diurnal variation
Sankoda et al., (2015) 4 beaches in Japan during summer 4.3–23.1 for mean concentrations
Sankoda et al., (2015) 4 beaches in Japan during winter 2.0–3.8 for mean concentrations
Total Measurements 122 30 46 79 35
Suggested Citation: "Appendix C: UV Filter Water and Sediment Occurrence Data." National Academies of Sciences, Engineering, and Medicine. 2022. Review of Fate, Exposure, and Effects of Sunscreens in Aquatic Environments and Implications for Sunscreen Usage and Human Health. Washington, DC: The National Academies Press. doi: 10.17226/26381.
Octinoxate Avobenzone Dioxybenzone Ensulizole Padimate O Reported as Total Organic Titanium Dioxide (µg/L) Zinc Oxide(µg/L)
0.1–31
4.1–13.3
ND–106 and illustrates diurnal variation
210–1,080 for mean concentrations
11–20 for mean concentrations
92 32 36 5 49 16 4 3
Suggested Citation: "Appendix C: UV Filter Water and Sediment Occurrence Data." National Academies of Sciences, Engineering, and Medicine. 2022. Review of Fate, Exposure, and Effects of Sunscreens in Aquatic Environments and Implications for Sunscreen Usage and Human Health. Washington, DC: The National Academies Press. doi: 10.17226/26381.

TABLE C.2 Spatial Analysis of Oxybenzone Measurements

Citation Location Oxybenzone (µg/L) Environment Classification Intensity of Source
Group A: Measurements > 1,000 ng/l
Bargar et al., 2015 Trunk Bay, USVI 6,073 Beach Swimming beach frequented by tourists
Bargar et al., 2015 Hawksnest Bay, USVI > 1,000; < 10,000 Beach Swimming beach frequented by tourists
Downs et al., 2021 Hanauma Bay, HI 30–27,880 with 40% > 1,000 Beach At beach within bathing area with high density
Tsui et al., 2014b Hong Kong Harbor 39–5,429 Beach Considered highly polluted; highest values associated with a popular beach
Bratcovics et al., 2015 Fishing Pier at Folly Beach area, SC ND–2,203; summer average = 1,533 Beach Park with family amenities
Bratkovics and Sapozhnikova, 2015 Wash Out Beach at Folly Beach, SC ND–1,766; summer average = 787 Beach Mostly residential popular local beach
Downs et al., 2016 Trunk Bay, USVI 580,000–1,395,000 Beach ~180 in water; ~130 on beach at time of sampling
Kung et al., 2018 Wanlitong Beach, Taiwan; one summer sampling event 1,233 Beach Popular beach
Schaap and Slijkerman, 2018 Sorobon, Bonaire. August 1,540 Beach Higher beach use in August
Tashiro and Kameda, 2013 Tropical Beach, Okinawa, Japan 2.2–1,258 Beach Popular beach
Bratcovics et al., 2015 County Park and beach on Folly Island, SC ND–2,126; summer average = 1,264 Beach Park with family amenities; may receive inputs from adjacent inlet
Tarazona et al., 2010 3 beaches on Mediterranean coast of Spain in summer 1,340–3,300 Beach Popular beach areas in summer months
Downs et al., 2016 Hawknest Bay, USVI 75,000–95,000 Beach 230 people on day of sampling
Sánchez Rodríguez et al., 2015 Beaches in the Canary Islands over 1 year at beach AM 91.0 (median); 12.7–2675.7 Beach Most touristic activity is focused
Sánchez Rodríguez et al., 2015 Beaches in the Canary Islands over 1 year at beach MG 343.2 (median); 54.2–3316.7 Beach Most touristic activity is focused
Total Intensity of Spatial Characteristics
Group B: Measurements 100–999 ng/l
Bargar et al., 2015 Cinnamon Bay, USVI > 100; < 1,000 Beach Swimming beach frequented by tourists
Bargar et al., 2015 Maho Bay, USVI > 100; < 1,000 Beach Moderate tourist
Lee Blaney, Presentation to Committee Chester River, Chesapeake Bay, MD ~50–~125 River Rural watershed
Lee Blaney, Presentation to Committee Lower Eastern Shore, Chesapeake Bay, MD ~50–~150 River Rural watershed
Suggested Citation: "Appendix C: UV Filter Water and Sediment Occurrence Data." National Academies of Sciences, Engineering, and Medicine. 2022. Review of Fate, Exposure, and Effects of Sunscreens in Aquatic Environments and Implications for Sunscreen Usage and Human Health. Washington, DC: The National Academies Press. doi: 10.17226/26381.
Proximity to Source Residence Time # High # Moderate # Low
Orange: High, Yellow: Moderate, Blue: Low
Along beach; nearshore Low tidal range; semi enclosed 3 0 0
Along beach; nearshore Low tidal range; semi enclosed 3 0 0
At the beach Low tidal amplitude in semi-enclosed bay 3 0 0
Adjacent to sources and receives polluted inflows Moderate mixing open to sea 2 1 0
At beach Moderate tide; open face to ocean, higher energy 2 1 0
At beach Moderate tide; open face to ocean, higher energy 2 1 0
Close proximity to beach and coral reef Low tidal range; semi enclosed 3 0 0
Along beach Low to moderate tidal amplitude; semi enclosed bay but somewhat exposed 2 1 0
Close to beach Small tidal amplitude; semi enclosed bay 3 0 0
Close to beach Low to moderate tidal amplitude; semi enclosed bay 2 1 0
At beach Moderate tide; open face to ocean, higher energy 2 1 0
Within swimming area Exposed to the open sea with low tidal range
Close proximity to beach and coral reef Low tidal range; semi enclosed 3 0 0
At beach Semi-enclosed; moderate tides 3 0 0
At beach Semi-enclosed; moderate tides 3 0 0
21 3 0
Close to beach Low tidal amplitude; somewhat exposed to open water 2 1 0
Close to beach Small tidal amplitude; semi enclosed bay 2 1 0
Within watershed with diffuse sources River flow and low/moderate tide 0 3 0
Within watershed with diffuse sources River flow and low/moderate tide 0 3 0
Suggested Citation: "Appendix C: UV Filter Water and Sediment Occurrence Data." National Academies of Sciences, Engineering, and Medicine. 2022. Review of Fate, Exposure, and Effects of Sunscreens in Aquatic Environments and Implications for Sunscreen Usage and Human Health. Washington, DC: The National Academies Press. doi: 10.17226/26381.
Citation Location Oxybenzone (µg/L) Environment Classification Intensity of Source
Horricks et al., 2019 Grand Anse Beach, Grenda 123 Beach Main tourist beach
Kung et al., 2018 Houwan Beach, Taiwan; one summer sampling event 566 Beach Popular beach
Kung et al., 2018 Houbiu Beach, Taiwan; one summer sampling event 118 Beach Popular beach
Kung et al., 2018 South Bay, Taiwan; one summer samplingevent 230 Beach Popular beach
Kung et al., 2018 Small Bay, Taiwan; one summer samplingevent 216 Beach Popular beach
Langford and Thomas, 2008 Sandvika Beach, Baerum, Norway in July at 3 locations 13.4–439.9 Beach In bathing area with reported ~200 people (mostly children) at two of the locations
Langford and Thomas, 2008 Huk Beach, near Oslo Norway 5.4–32.1 Beach No specifics in paper but apears to be a beach with moderate activity
O’Malley et al., 2021 Enogerra Reservoir, Australia based on bar charts and reported values ~200–~700 Lake (Reservoir) Recreational reservoir
Tsui et al., 2014b New York City including Jamaica Bay, Upper New York Bay, and East River near WWTP discharges 23–178 Coastal Receives discharges from multiple sources
Tsui et al., 2014b Los Angeles at Huntington Beach 227–601 Beach Popular beach
Tsui et al., 2014b Shantou, China at beach 55–188 Beach Popular beach
Tsui et al., 2014b Chao Phraya River at Bangkok, Thailand 86–116 River Large watershed with agricultural and urban inputs as well as effluents
Li et al., 2018 Popular beaches along coastline of Shenzhen, China ND–172 Beach Popular beaches
Sánchez Rodríguez et al., 2015 Beaches in the Canary Islands over 1 year at beach PR 238.7 (median); 32.8–979.8 Beach Most touristic activity is focused
Tashiro and Kameda, 2013 Emerald Beach, Okinawa, Japan ND–141 Beach Popular beach
Tashiro and Kameda, 2013 Sunset Beach, Okinawa, Japan 10–448 Beach Popular beach
Tashiro and Kameda, 2013 Araha Beach, Okinawa, Japan 0.5–428 Beach Popular beach
Grabicova et al., 2013 Recreational ponds in Czech Republic 21–550 Lake (Reservoir Recreational pond
Tovar-Sanchez, 2013 Popular beaches on Majorca Island, Spain, sampled two days in August 76–155 with max at one beach of 400 at midday to afternoon Beach Popular beach in summer
Suggested Citation: "Appendix C: UV Filter Water and Sediment Occurrence Data." National Academies of Sciences, Engineering, and Medicine. 2022. Review of Fate, Exposure, and Effects of Sunscreens in Aquatic Environments and Implications for Sunscreen Usage and Human Health. Washington, DC: The National Academies Press. doi: 10.17226/26381.
Proximity to Source Residence Time # High # Moderate # Low
Orange: High, Yellow: Moderate, Blue: Low
Near beach Low tidal amplitude; semi enclosed but open to ocean 2 1 0
Near beach Low to moderate tidal amplitude; semi enclosed bay 2 1 0
Near beach Low to moderate tidal amplitude; semi enclosed bay but more exposed 2 1 0
Near beach Low to moderate tidal amplitude; somewhat exposed 2 1 0
Near beach Low to moderate tidal amplitude; somewhat exposed 2 1 0
Within bathing area Semi-enclosed area with limited flushing 3 0 0
Within the bathing area Open to flushing with the fjord, considered in the paper to be a higher energy area than other sampled beach 1 2 0
At the beach Low energy 3 0 0
Adjacent to many diffuse sources including wastewater effluents Part of this area (Jamaica Bay) is poorly flushed and receives effluent 2 1 0
Within bathing area Open to the ocean and higher energy 2 0 1
Within bathing area Moderate mixing 2 1 0
Adjacent and downstream of diffuse sources Dilution within a large river 3 0 0
Within bathing area Exposed to sea and expected to have moderate mixing and transport 2 1 0
At beach Semi-enclosed; moderate tides 3 0 0
Near beach Low to moderate tidal amplitude; semi enclosed bay 2 1 0
Near beach Low to moderate tidal amplitude; semi enclosed bay 2 1 0
Near beach Low to moderate tidal amplitude; open to the sea 2 1 0
Near beach Pond with long residence time 3 0 0
Within swimming area Moderate, semi-enclosed 2 1 0
Suggested Citation: "Appendix C: UV Filter Water and Sediment Occurrence Data." National Academies of Sciences, Engineering, and Medicine. 2022. Review of Fate, Exposure, and Effects of Sunscreens in Aquatic Environments and Implications for Sunscreen Usage and Human Health. Washington, DC: The National Academies Press. doi: 10.17226/26381.
Citation Location Oxybenzone (µg/L) Environment Classification Intensity of Source
Bratcovics et al., 2015 Coast Guard Stations Estuarine Research Reserve, SC ND–467: summer average = 233 Beach Some beach use
Nguyen et al., 2011 3 locations along the Ligurion coast (Italy) sampled monthly June–August 2010 ND–118 Coastal Not specified but Ligurion Sea is bordered by several cities
He et al., 2019a Manokin River, Chesapeake Bay, MD 52.7–113.7 River Rural watershed
Mitchelmore et al., 2019 Waikiki Beach Hawaii Nearshore 8.8–142.7 Beach Popular beach area; unclear on number of people
Mitchelmore et al., 2019 Waikiki Beach Hawaii–offshore 9.4–73.1 Coastal Popular beach area; unclear on number of people
Bratcovics et al., 2015 Myrtle Beach, SC ND–575; summer average = 329 Beach Popular beach area; unclear on number of people
Bratcovics et al., 2015 North Inlet National Estuarine Research Reserve, SC ND–138; summer average = 34 River Drains watershed
Sánchez Rodríguez et al., 2015 Beaches in the Canary Islands over 1 year at beach AL 3.7 (median); < 1.4–158.0 Beach Local community beach
Sánchez Rodríguez et al., 2015 Beaches in the Canary Islands over 1 year at beach CA 9.6 (median); < 1.4–182.6 Beach Local community beach
Total Intensity of Spatial Characteristics
Group C: 10–99 ng/l
Gago-Ferrero et al., 2013 Llobregat River, NE Spain for 5 samples in 2011 ND–37.8 River Watershed has diffuse sources
Pedrouzo et al., 2010 3 rivers in Catalonia, Spain; part of methods development 6–28 River Rivers drain agricultural and urban areas
Wick et al., 2010 Sampling in 2 streams located downstream from the last discharge of a WWTP in September ND–47 River WWTPs upstream
Balmer et al., 2005 Lake Greifensee, Switzerland surface 20–30 Lake Inputs of UV filters are expected; important recreational area
Balmer et al., 2005 Lake Hüttnersee, Switzerland surface 23–35 Lake The number of bathers relative to the lake volume and water throughflow is considered high
Tsui et al., 2014b Tokyo Bay 24–86 Coastal Diffuse sources
Langford and Thomas, 2008 Near offshore WWTP outfall (VEAS) from city of Oslo, Norway, July ND–15.5 Coastal Near WWTP outfall located offshore of Oslo Norway
Langford and Thomas, 2008 Open waters of fjord off Baerum and Oslo, Norway, July 5.4–32.1 Coastal Located in open waters of fjord
Suggested Citation: "Appendix C: UV Filter Water and Sediment Occurrence Data." National Academies of Sciences, Engineering, and Medicine. 2022. Review of Fate, Exposure, and Effects of Sunscreens in Aquatic Environments and Implications for Sunscreen Usage and Human Health. Washington, DC: The National Academies Press. doi: 10.17226/26381.
Proximity to Source Residence Time # High # Moderate # Low
Orange: High, Yellow: Moderate, Blue: Low
Near beach Moderate tide and river flow 0 3 0
Offshore location Open water with higher energy 0 2 1
Within watershed with diffuse sources River flow and low/moderate tide 0 3 0
Bathing area of beach Low tidal amplitude; open face to ocean, higher energy 1 2 0
Offshore location Low tidal amplitude; open face to ocean, higher energy 0 2 1
At beach Moderate tide; open face to ocean, higher energy 1 2 0
Represents sources entering the watershed Moderate tide and river flow 0 3 0
At beach Open to ocean; moderate tides 1 1 1
At beach Open to ocean; moderate tides 1 1 1
50 41 5
Adjacent and downstream from diffuse sources Mixing and dilution in large river 0 3 0
Adjacent and downstream from diffuse sources Major rivers offering dilution 0 3 0
Downstream Some dilution in the streams 0 3 0
Within recreational waters High input to volume with P/Q of 0.303 persons/ m3/d 1 2 0
Remote location but used heavily for recreation P/Q of 0 people/m3/d; short residence time of ~120 days 2 0 1
Adjacent to but distant from sources Moderate flushing 0 3 0
Various distances from outfall; sampling was at the surface and effluent subject to initial dilution Deep water high energy area; sampling was near the surface 1 1 1
Distant from recreational areas and discharges High energy flushing 0 0 3
Suggested Citation: "Appendix C: UV Filter Water and Sediment Occurrence Data." National Academies of Sciences, Engineering, and Medicine. 2022. Review of Fate, Exposure, and Effects of Sunscreens in Aquatic Environments and Implications for Sunscreen Usage and Human Health. Washington, DC: The National Academies Press. doi: 10.17226/26381.
Citation Location Oxybenzone (µg/L) Environment Classification Intensity of Source
Li et al., 2018 Less popular or undeveloped beaches along the Shenzhen, China coastline ND–28.7 Beach Less popular beach
Bargar et al., 2015 Leinster Bay, USVI ND–< 100 Beach Moderate tourist
Bargar et al., 2015 Brown Bay, USVI 1.6–133 Beach Low tourist
Bargar et al., 2015 Great Lameshure Bay, USVI ND–< 100 Beach Low tourist
da Silva et al., 2015 Tieta River at Jau Brazil (river water intake) 6 months of sampling ND–24 River Pollution is known to exist well upriver but is retained to some extent by reservoirs such as the Barra Bonita Reservoir
Downs et al., 2016 Maunalua Bay, Oahu, HI > 100–19,200 Beach Collected within a public swimming area
Ekpeghere et al., 2016 Rivers in South Korea determined from box plots. Rivers include Nakdong River (nine sites), Guemho River (one site) and Nam River (one site) ~5–~50 River Paper reports continuous inputs to the rivers
Tsui et al., 2014b Chaozhou, China at beach 37–49 Beach Popular beach
Tsui et al., 2014b Arctic Ocean and Chukchi Sea 17–33 Coastal No major direct sources
Fent et al., 2010 River Glatt below a WWTP, Switzerland 56 and 68 River River downstream of WWTP
He et al., 2019a Chester River, Chesapeake Bay, MD 52–96 River Rural watershed
Emnet et al., 2015 Erubus Bay near a research station, Antarctica 2.6–88.4 Coastal Remote location but near a research station
He et al., 2019a Holland Straights, Chesapeake Bay, MD 40.4–59.3 Coastal Low contact recreation
He et al., 2019a Kitts Creek, Chesapeake Bay, MD 31.1–32 River Rural watershed
Kung et al., 2018 Boli River Estuary, Taiwan; one summer samplingevent 41.4 River Diffuse, mixed, river flow
Kung et al., 2018 Scichong River Estuary, Taiwan; 1 summer sampling event 45.4 River Diffuse, mixed, river flow
Kung et al., 2018 Baisha Beach, Taiwan; 1 summer sampling event 23 Beach Popular beach
Kung et al., 2018 Big Bay, Taiwan; 1 summer sampling event 18.8 Beach Popular beach
Labille et al., 2020 Three beaches along French Mediterranean in the bathing area (over 1 day) < 1–78 Beach Active on day of sampling
Labille et al., 2020 Three beaches along French Mediterranean beyond bathing area (over 1 day) < 1–26.7 Beach Active on day of sampling
Suggested Citation: "Appendix C: UV Filter Water and Sediment Occurrence Data." National Academies of Sciences, Engineering, and Medicine. 2022. Review of Fate, Exposure, and Effects of Sunscreens in Aquatic Environments and Implications for Sunscreen Usage and Human Health. Washington, DC: The National Academies Press. doi: 10.17226/26381.
Proximity to Source Residence Time # High # Moderate # Low
Orange: High, Yellow: Moderate, Blue: Low
Within bathing areas Relatively exposed and higher energy 1 2 0
Close proximity to beach Low tidal range; semi enclosed 2 1 0
Close proximity to beach Low tidal range; semi enclosed 2 0 1
Close proximity to beach Low tidal range; semi enclosed 2 0 1
Downstream of Barra Bonita Reservoir and upstream sources One of the largest rivers in S≥o Paulo estado (state) so large flow expected 0 2 1
Close proximity to beach Low tidal range; open face to ocean 2 1 0
Adjacent Mixing and advection in river flow. Nakdong River is one of the longest and largest rivers in South Korea; the other two rivers are among its tributaries 2 0 1
Within bathing areas Exposed with higher energy 2 1 0
Distant from known sources High energy environment 0 0 3
Receives point and nonpoint sources Mixed within small river system: 9 m3/s 1 2 0
Within watershed with diffuse sources River flow and low/moderate tide 0 3 0
Near a research station but relatively remote Open to the ocean 0 2 1
Distant from nonpoint sources Open water 0 2 1
Within watershed with diffuse sources River flow and low/moderate tide 0 3 0
Many sources but sampling is distant from them River flow with mixing at delta 0 1 2
Many sources but sampling is distant from them River flow with mixing at delta 0 1 2
Near beach Small tidal amplitude but exposed to open water 2 0 1
Near beach Small tidal amplitude but exposed to open water 2 0 1
At beach Open to sea 2 1 0
At beach Open to sea 2 1 0
Suggested Citation: "Appendix C: UV Filter Water and Sediment Occurrence Data." National Academies of Sciences, Engineering, and Medicine. 2022. Review of Fate, Exposure, and Effects of Sunscreens in Aquatic Environments and Implications for Sunscreen Usage and Human Health. Washington, DC: The National Academies Press. doi: 10.17226/26381.
Citation Location Oxybenzone (µg/L) Environment Classification Intensity of Source
Kasprzyk-Hordern et al., 2008a,b River Taff (South Wales) in segment above and below wastewater discharges, 4 locations reported, based on several months of sampling from Nov 2006 to Aug 2007 ND–44 River Water bodies received domestic wastewater
Kameda et al., 2011 Rivers (18) and streams (2) in Japan considered polluted to varying degrees with domestic sewage and other pollutants sampled in August and September 2008 ND–41 River Water bodies received domestic wastewater
Tovar-Sanchez, 2013 Undeveloped coastal location on Majorca Island, Spain–1 day in September 36 Coastal Remote location
Wu et al., 2013 2 rivers in northern Taiwan that receive direct discharges of municipal wastewater 12.3–15.4 River Rivers receive municipal wastewater
Rodil et al., 2008a 2 recreational lakes around Leipzig Germany in June 2007 27–55 Lake Recreational lakes but early in the season
Rodil et al., 2008a 2 rivers around Leipzig Germany in May 2007 ND–30 River Drains agricultural and urban areas
Tsui et al., 2017 Ung Kong, Hong Kong for wet and dry seasons 25.8 (wet); 29.1 (dry) Coastal Coral reef adjacent to remote island; diver destination
Tsui et al., 2017 Sharp Island, Hong Kong for wet and dry seasons 24.4 (wet); 31.7 (dry) Coastal Coral reef adjacent to remote island; diver destination
Tsui et al., 2017 Wu Pai, Hong Kong for wet and dry seasons 13.9 (wet); 13.8 (dry) Coastal Coral reef adjacent to remote island; diver destination
Tsui et al., 2017 Sung Kong, Hong Kong for wet and dry seasons 13.2 (wet) Coastal Coral reef adjacent to remote island; low degree of visitation due to strong currents
Grabicova et al., 2013 Rivers with pollution in Czech Republic 16–67 River Rivers known to have pollution
da Silva et al., 2015 Araraquara or Tietje Rivers at Araraquara, Brazil (river water intake) monthly sampling over 1 y ND–38 River Urban and agricultural development in watershed; no information on recreational use
da Silva et al., 2015 Tiete River at Bauru (river water intake) 6 months sampling ND–28 River Pollution is known to exist well upriver but is retained to some extent by reservoirs such as the Barra Bonita Reservoir
da Silva et al., 2015 Feij≥o River at S≥o Carlos Brazil (river water intake) 6 months of sampling ND–44 River Urban and agricultural development in watershed; no information on recreational use
Mitchelmore et al., 2019 Kaneohe Bay Hawaii Shallow 4.7–11.3 Beach High impact tourist, scuba and recreation site
Suggested Citation: "Appendix C: UV Filter Water and Sediment Occurrence Data." National Academies of Sciences, Engineering, and Medicine. 2022. Review of Fate, Exposure, and Effects of Sunscreens in Aquatic Environments and Implications for Sunscreen Usage and Human Health. Washington, DC: The National Academies Press. doi: 10.17226/26381.
Proximity to Source Residence Time # High # Moderate # Low
Orange: High, Yellow: Moderate, Blue: Low
Upstream and downstream Large river with high dilution from receiving waters 1 1 1
Downstream Moderate with dilution from receiving waters 1 2 0
Remote Open to the sea 0 0 3
Downstream Moderate dilution expected following initial dilution 0 3 0
Likely in bathing area Lakes have longer residence times 0 3 0
Adjacent and down river from diffuse sources Dilution afforded by the river flow 0 3 0
At coral reef Open to ocean; expected higher energy 0 2 1
At coral reef Open to ocean; expected higher energy 0 2 1
At coral reef Open to ocean; expected higher energy 0 2 1
At coral reef Strong currents; high energy environment 0 1 2
Downstream Mixed with river flow 0 2 1
Watershed adjacent to river Smaller river system 0 3 0
Downstream of Barra Bonita Reservoir and upstream sources One of the largest rivers in S≥o Paulo estado (state) so large flow expected 0 2 1
Drains large watershed River flow would cause mixing and advection 0 3 0
Near surface Low tidal amplitude; open face to ocean, higher energy 0 3 0
Suggested Citation: "Appendix C: UV Filter Water and Sediment Occurrence Data." National Academies of Sciences, Engineering, and Medicine. 2022. Review of Fate, Exposure, and Effects of Sunscreens in Aquatic Environments and Implications for Sunscreen Usage and Human Health. Washington, DC: The National Academies Press. doi: 10.17226/26381.
Citation Location Oxybenzone (µg/L) Environment Classification Intensity of Source
Mitchelmore et al., 2019 Kaneohe Bay Hawaii Deep 0.1–48.1 Coastal Tourist, scuba and recreation site
Sánchez Rodríguez et al., 2015 Beaches in the Canary Islands over 1 year at beach MP 4.6 (median); < 1.4–27.1 Beach Most touristic activity is focused
Tsui et al., 2019 Coastal Hong Kong and adjacent South China Sea (concentrations decrease with distance seaward) 2.2–36.7 Coastal Coastal and open ocean locations
Fisch et al., 2017 Rivers draining to Baltic and coastline, Germany ND–11.4 River Rivers known to have pollution
Total Intensity of Spatial Characteristics
Group D: < 10 ng/l
Kasprzyk-Hordern et al., 2008b River Ely (South Wales, UK) in segment above and below wastewater discharges, 4 locations reported, based on several months of sampling from Nov 2006 to Aug 2007 ND River Water bodies received domestic wastewater
Balmer et al., 2005 Lake Zürichsee, Switzerland Surface 10–20; deep (20 m) 10–11 Lake Significant direct and indirect
Balmer et al., 2005 Lake Jörisee, Switzerland < 2 Lake Negligible input from watershed or recreation
Allison et al., 2018 3 estuaries flowing into Port Philp Bay, around Melbourne, Australia (4 water grab samples) in August 2011 (winter) 4.3–7.1 River Small WWRP in upper catchments, urban runoff, recreational use low because of winter
Bargar et al., 2015 Trunk Bay, USVI at 210 m from shoreline 2.7 Beach Popular beach but rain kept people away
Wick et al., 2010 Rhine River in Koblenz, Germany in March 2008 ND River Diffuse sources along the river
Downs et al., 2016 Caneel Bay, USVI ND Beach 17 people on beach over 48h
Downs et al., 2016 Kapalua Bay, Maui, HI ND Beach 14 swimmers on day of sampling
Downs et al., 2016 Kahekili Beach, Maui, HI ND Beach 71 swimmers within 200 m at time of sampling
Horricks et al., 2019 Grand Anse Bay, Grenada deep 7 Coastal Diving
Horricks et al., 2019 Grand Mal, Grenada surface 7 Coastal Nearer shore
Horricks et al., 2019 Grand Mal, Grenada deep ND Coastal Diving
Horricks et al., 2019 True Blue, Grenada surface ND Beach Nearer shore
Suggested Citation: "Appendix C: UV Filter Water and Sediment Occurrence Data." National Academies of Sciences, Engineering, and Medicine. 2022. Review of Fate, Exposure, and Effects of Sunscreens in Aquatic Environments and Implications for Sunscreen Usage and Human Health. Washington, DC: The National Academies Press. doi: 10.17226/26381.
Proximity to Source Residence Time # High # Moderate # Low
Orange: High, Yellow: Moderate, Blue: Low
At depth Low tidal amplitude; open face to ocean, higher energy 0 2 1
At beach Open to ocean; moderate tides 2 1 0
Some locations at distance from source areas Open ocean areas 0 3 0
Downstream Mixed with river flow 0 2 1
30 78 33
Upstream and downstream Small shallow river with limited dilution 1 2 0
Adjacent to or downstream of diffuse sources P/Q of 0.043 people/m3/d 1 2 0
Distant from sources P/Q of 0 people/m3/d 0 0 3
Downstream of sources Mixing with river water and estuarine flushing with the Bay 0 3 0
Close proximity of beach Low tidal range; semi enclosed 2 0 1
Adjacent to or downstream of diffuse sources Large river with associated dilution 0 2 1
Close proximity to beach and coral reef Low tidal range; semi enclosed 2 0 1
Close proximity to beach and remnant coral Low tidal range; semi enclosed 2 0 1
Close proximity of beach Low tidal range; open face to ocean 1 2 0
Offshore location Exposed to open ocean 0 0 3
Considered upcurrent of source areas Exposed to open ocean 0 1 2
Considered upcurrent of source areas Exposed to open ocean 0 0 3
Near beach Low tidal range; semi enclosed 2 1 0
Suggested Citation: "Appendix C: UV Filter Water and Sediment Occurrence Data." National Academies of Sciences, Engineering, and Medicine. 2022. Review of Fate, Exposure, and Effects of Sunscreens in Aquatic Environments and Implications for Sunscreen Usage and Human Health. Washington, DC: The National Academies Press. doi: 10.17226/26381.
Citation Location Oxybenzone (µg/L) Environment Classification Intensity of Source
Horricks et al., 2019 Quarantine Reef, Grenada surface ND Coastal Divers
Horricks et al., 2019 Quarantine Reef, Grenada deep ND Coastal Divers
Mitchelmore et al., 2019 Ka’a’awa Bay, Hawaii Nearshore 2.6–7.1 Coastal Area of low recreational use and remote from communities
Mitchelmore et al., 2019 Ka’a’awa Bay, Hawaii–offshore 0.1–7.5 Coastal Area of low recreational use and remote from communities
Rohée et al., 2019 Villeneuve de la Raho Lake, France < 5 Lake Popular recreational area
Schaap and Slijkerman, 2018 Sorobon, Bonaire November, 2018 < 10 Beach Lower beach use due to rain
Schaap and Slijkerman, 2018 Mangrove Lac Bay, Bonaire during August 10 Coastal Nearby beach with elevated levels
Schaap and Slijkerman, 2018 Cai Reef, Bonaire < 10 Coastal Divers, at distance from beach with elevated levels
Li et al., 2018 Drinking water reservoir in Shenzhen, China 9.2 Lake Area of low recreational use and remote from communities
Tashiro and Kameda, 2013 Shirahi River, Okinawa, Japan ND–9 River Diffuse, mixed, river flow
Tashiro and Kameda, 2013 CR coral reef site 660 m from Araha Beach, Okinawa, Japan ND–0.4 Coastal Divers
Tashiro and Kameda, 2013 BR Reef Site, 520 m from Emerald Bay, Okinawa, Japan ND–3.8 Coastal Divers
Rodil et al., 2012 6 locations along Mero River in Galicia Spain, samples were collected over a year ND River River drains agricultural and urban areas
Total Intensity of Spatial Characteristics
Suggested Citation: "Appendix C: UV Filter Water and Sediment Occurrence Data." National Academies of Sciences, Engineering, and Medicine. 2022. Review of Fate, Exposure, and Effects of Sunscreens in Aquatic Environments and Implications for Sunscreen Usage and Human Health. Washington, DC: The National Academies Press. doi: 10.17226/26381.
Proximity to Source Residence Time # High # Moderate # Low
Orange: High, Yellow: Moderate, Blue: Low
Offshore of beaches, periodic divers Exposed to open ocean 0 0 3
Offshore of beaches, periodic divers Exposed to open ocean 0 0 3
Within bathing area and near fringe reef Low tidal amplitude; open face to ocean, higher energy 1 0 2
Offshore Low tidal amplitude; open face to ocean, higher energy 0 0 3
At beach 2 1 0
Near beach Small tidal amplitude; semi enclosed bay 2 0 1
At distance from beach Small tidal amplitude; semi enclosed bay 1 1 1
Dive site Open to ocean, adjacent to channel 0 1 2
Sources not proximal Moderate mixing and residence time as this is a reservoir 0 2 1
Many sources but sampling is distant from them River flow with mixing at delta 0 1 2
Dive site distant from beach Exposed to open ocean 0 1 2
Dive site distant from beach Exposed to open ocean 0 1 2
Adjacent to diffuse sources Moderate dilution with river flow 0 3 0
17 24 37
Suggested Citation: "Appendix C: UV Filter Water and Sediment Occurrence Data." National Academies of Sciences, Engineering, and Medicine. 2022. Review of Fate, Exposure, and Effects of Sunscreens in Aquatic Environments and Implications for Sunscreen Usage and Human Health. Washington, DC: The National Academies Press. doi: 10.17226/26381.

TABLE C.3 Reported Concentrations of UV Filters in Sediments (ng/g)

Citation Location Oxybenzone Homosalate Octocrylene
Baron et al., 2013 Conception Bay, Chile ND
Baron et al., 2013 San Vencente Bay ND–1.42
Baron et al., 2013 Lenga Estuary, Chile ND–2.96
Baron et al., 2013 Biobio River, Chile ND–1.05
Baron et al., 2013 Coronel Bay, Chile ND
Baron et al., 2013 West Coastal Line, Colombia ND–2.52
Baron et al., 2013 Bocas de Ceniza and Mallorquin Swamp, Colombia ND–4.85
Baron et al., 2013 Magdalena River, Colombia ND–5.38
Allinson et al., 2018 3 estuaries flowing into Port Philp Bay, around Melbourne, Austrailia (4 water grab samples) in August 2011 (winter) ND ND
Combi et al., 2016 Northern Adriatic ND–0.23 4–40.7
Combi et al., 2016 Central Adriatic ND–0.1 0.8–33.7
Combi et al., 2016 Southern Adriatic 0.9–19.0
Díaz-Cruz et al., 2019 Evrotas River, Greece <LOQ 0.1–0.7
Fagervold et al., 2019 Bay of Banyuls-sur-Mer, France ~ 10–50
Fagervold et al., 2019 Villeneuve de la Raho Lake, France ~ 10–20
Gago-Ferrero et al., 2015 Guadalquivir River, Spain ND–22.5
Gago-Ferrero et al., 2011 Ebro River, Spain up to 27 up to 2,400
Kaiser et al., 2012b Lakes in RhineMain area near Frankfurt up to 3.6 up to 642
Kaiser et al., 2012b Rivers in RhineMain area near Frankfurt ND up to 25.2
Mizukawa et al., 2019 Palmital River, Brazil ND–32.7 25.9–117
Mizukawa et al., 2019 Atuba River, Brazil <LOQ–36.8 <LOQ–322.2
Mizukawa et al., 2019 Belem River, Brazil <LOQ–50.9 48.5–313.8
Mizukawa et al., 2019 Iguaçu River, Brazil <LOQ–67.2 <LOQ–160.8
Astel et al., 2020 Southern Baltic beach sediments <LOD–0.074
Pintado-Herrera etal., 2017 Cadiz Bay, Atlantic coast (Andalusia, Spain) 0.1–1.6 0.1–9.8 4.6–43.6
Pintado-Herrera etal., 2017 Huelva Estuary, Atlantic coast (Andalusia, Spain) 0.5–1.2 0.1–2.4 1.7–38
Sánchez-Brunete etal., 2011 Sediments from 5 rivers in Spain ND ND
Sánchez-Brunete etal., 2011 Sediment from marine sediment, Spain ND ND
Suggested Citation: "Appendix C: UV Filter Water and Sediment Occurrence Data." National Academies of Sciences, Engineering, and Medicine. 2022. Review of Fate, Exposure, and Effects of Sunscreens in Aquatic Environments and Implications for Sunscreen Usage and Human Health. Washington, DC: The National Academies Press. doi: 10.17226/26381.
Octisalate Octinoxate Avobenzone Dioxybenzone Padimate O Reported as Total Organic
ND
ND
ND
ND
ND
ND–17.8
ND–39.0
ND–47
ND ND–17.6 ND
1–10.4
0.9–6.9
1.3–10
7.5–22.9
up to 4.4
up to 6.8
up to 3.4
ND–43 ND <LOQ
ND–121.2 ND <LOQ
< LOQ–166.8 ND–<LOQ <LOQ
< LOQ–129.6 ND–<LOQ <LOQ
0.2–7.7 0.4–23.8 8–74.4
4.3–6.4 0.4–17 10.7–58.2
ND–20
13.3
Suggested Citation: "Appendix C: UV Filter Water and Sediment Occurrence Data." National Academies of Sciences, Engineering, and Medicine. 2022. Review of Fate, Exposure, and Effects of Sunscreens in Aquatic Environments and Implications for Sunscreen Usage and Human Health. Washington, DC: The National Academies Press. doi: 10.17226/26381.
Citation Location Oxybenzone Homosalate Octocrylene
Mitchelmore et al., 2019 Waikiki Beach, HI—nearshore 0.02–0.72 ND–9.08 0.02–27.54
Mitchelmore et al., 2019 Waikiki Beach, HI—offshore ND–0.02 ND–8.74 ND–0.98
Mitchelmore et al., 2019 Kaneohe Bay, HI—shallow ND–0.55 2.56–20.84 0.59–10.48
Mitchelmore et al., 2019 Kaneohe Bay, HI—deep ND–4.49 5.59–38.84 1.38–7.36
Mitchelmore et al., 2019 Ka’a’awa Bay, HI—nearshore ND–0.75 ND–5.53 ND–0.01
Mitchelmore et al., 2019 Ka’a’awa Bay, HI—offshore ND–0.02 ND–5.86 ND–0.02
He et al., 2019a Holland Straights, Chesapeake Bay, MD 8.2–10.1 50.4–74.2 0.9–2.9
He et al., 2019a Kitts Creek, Chesapeake Bay, MD 8.1–9.4 47.6–48.8 0.2–1.3
He et al., 2019a Manokin River, Chesapeake Bay, MD 6.9–10.8 20.0–60.5 0.2–0.8
Amine et al., 2012 3 rivers in Lebanon flowing to eastern Mediteranean, multiple samples from 3 months in 2010 and 2011 ~15–~95 with max of 128
Amine et al., 2012 Coastal sediments off mouths of 3 rivers in Lebanon, multiple samples from 3 months in 2010 and 2011 ~10–~65
Amine et al., 2012 Coastal sediments along El-Mina, Lebanon coastline influenced by sewage discharges ~40–~79
Amine et al., 2012 River sediments from Lez River, France downstream of a municipal wastewater discharge 32.8
Kameda et al., 2011 Rivers (18) and streams (2) in Japan considered polluted to varying degrees with domestic sewage and other pollutants sampled in August and September 2008 ND ND–26 ND–635
Rodil et al., 2008b 3 recreational lakes around Leipzig Germany in August 2007 61–93
Tsui et al., 2017 Sampling at coral habitats aroud Hong Kong in wet and dry periods: Wu Pai 9.8 (wet); 17 (dry) 2.6 (wet); ND
Tsui et al., 2017 Sampling at coral habitats aroud Hong Kong in wet and dry periods: Sharp Island 6.5 (wet); 8.1 (dry) 2.7 (wet); ND
Tsui et al., 2017 Sampling at coral habitats aroud Hong Kong in wet and dry periods: Ung Kong 6.1 (wet); 4.2 (dry) 2.1 (wet); ND
Tsui et al., 2017 Sampling at coral habitats aroud Hong Kong in wet and dry periods: Sung Kong 8.5 (wet) 3.1 (wet)
Tsui et al., 2015 Hong Kong—13 locations including Victoria Harbor and Sai Kung in August 1–39.8 ND 0.04–15.2
Tsui et al., 2015 Hong Kong—13 locations including Victoria Harbor and Sai Kung in February 2.5–2.5 ND 5–12.4
Tsui et al., 2015 Hong Kong—13 locations including Victoria Harbor and Sai Kung in June (wet) 0.05–10.2 ND 0.7–15.6
Tsui et al., 2015 Tokyo Bay—8 locations in July ND ND ND
Total Measurements 44 18 38
Suggested Citation: "Appendix C: UV Filter Water and Sediment Occurrence Data." National Academies of Sciences, Engineering, and Medicine. 2022. Review of Fate, Exposure, and Effects of Sunscreens in Aquatic Environments and Implications for Sunscreen Usage and Human Health. Washington, DC: The National Academies Press. doi: 10.17226/26381.
Octisalate Octinoxate Avobenzone Dioxybenzone Padimate O Reported as Total Organic
ND–7.96 0–0.08 ND–7.99 ND 0.56–41.32
ND–3.9 ND ND–0.08 ND 0.4–11.55
2.42–42.83 ND–31.43 0.48–7.73 ND 15.28–100.18
2.42–20.71 ND–7.79 ND–0.48 ND 24.87–72.49
ND–7.12 ND–0.05 ND–0.08 ND 0.3–12.73
ND–7.82 ND–0.08 ND ND 0.02–13.34
3.3–4.4
3.6–3.7
3.8–6.5
ND–35.8 with max of 45 ~1–~11 with max of 17.9
ND–~8 ~1–~4
~5–~8 ~5–~10
7.9 ND
ND ND–101 ND
14–34
ND
ND
ND
ND
ND 1.4–447 4.3–43.9 2.7–42.2 8–81.6
ND 0.8–291 5.5.–18.6 0.8–38.4 15.2–21.8
ND 0.6–119 4.3–16 2.4–62.2 1.5–150
ND 0.3–54.5 2.5–64.5 1.3–14.1 0.8–13.9
16 40 10 12 21 8
Suggested Citation: "Appendix C: UV Filter Water and Sediment Occurrence Data." National Academies of Sciences, Engineering, and Medicine. 2022. Review of Fate, Exposure, and Effects of Sunscreens in Aquatic Environments and Implications for Sunscreen Usage and Human Health. Washington, DC: The National Academies Press. doi: 10.17226/26381.

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Suggested Citation: "Appendix C: UV Filter Water and Sediment Occurrence Data." National Academies of Sciences, Engineering, and Medicine. 2022. Review of Fate, Exposure, and Effects of Sunscreens in Aquatic Environments and Implications for Sunscreen Usage and Human Health. Washington, DC: The National Academies Press. doi: 10.17226/26381.
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Suggested Citation: "Appendix C: UV Filter Water and Sediment Occurrence Data." National Academies of Sciences, Engineering, and Medicine. 2022. Review of Fate, Exposure, and Effects of Sunscreens in Aquatic Environments and Implications for Sunscreen Usage and Human Health. Washington, DC: The National Academies Press. doi: 10.17226/26381.
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Suggested Citation: "Appendix C: UV Filter Water and Sediment Occurrence Data." National Academies of Sciences, Engineering, and Medicine. 2022. Review of Fate, Exposure, and Effects of Sunscreens in Aquatic Environments and Implications for Sunscreen Usage and Human Health. Washington, DC: The National Academies Press. doi: 10.17226/26381.
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Suggested Citation: "Appendix C: UV Filter Water and Sediment Occurrence Data." National Academies of Sciences, Engineering, and Medicine. 2022. Review of Fate, Exposure, and Effects of Sunscreens in Aquatic Environments and Implications for Sunscreen Usage and Human Health. Washington, DC: The National Academies Press. doi: 10.17226/26381.
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Suggested Citation: "Appendix C: UV Filter Water and Sediment Occurrence Data." National Academies of Sciences, Engineering, and Medicine. 2022. Review of Fate, Exposure, and Effects of Sunscreens in Aquatic Environments and Implications for Sunscreen Usage and Human Health. Washington, DC: The National Academies Press. doi: 10.17226/26381.
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Suggested Citation: "Appendix C: UV Filter Water and Sediment Occurrence Data." National Academies of Sciences, Engineering, and Medicine. 2022. Review of Fate, Exposure, and Effects of Sunscreens in Aquatic Environments and Implications for Sunscreen Usage and Human Health. Washington, DC: The National Academies Press. doi: 10.17226/26381.
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Suggested Citation: "Appendix C: UV Filter Water and Sediment Occurrence Data." National Academies of Sciences, Engineering, and Medicine. 2022. Review of Fate, Exposure, and Effects of Sunscreens in Aquatic Environments and Implications for Sunscreen Usage and Human Health. Washington, DC: The National Academies Press. doi: 10.17226/26381.
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Suggested Citation: "Appendix C: UV Filter Water and Sediment Occurrence Data." National Academies of Sciences, Engineering, and Medicine. 2022. Review of Fate, Exposure, and Effects of Sunscreens in Aquatic Environments and Implications for Sunscreen Usage and Human Health. Washington, DC: The National Academies Press. doi: 10.17226/26381.
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Suggested Citation: "Appendix C: UV Filter Water and Sediment Occurrence Data." National Academies of Sciences, Engineering, and Medicine. 2022. Review of Fate, Exposure, and Effects of Sunscreens in Aquatic Environments and Implications for Sunscreen Usage and Human Health. Washington, DC: The National Academies Press. doi: 10.17226/26381.
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Suggested Citation: "Appendix C: UV Filter Water and Sediment Occurrence Data." National Academies of Sciences, Engineering, and Medicine. 2022. Review of Fate, Exposure, and Effects of Sunscreens in Aquatic Environments and Implications for Sunscreen Usage and Human Health. Washington, DC: The National Academies Press. doi: 10.17226/26381.
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Suggested Citation: "Appendix C: UV Filter Water and Sediment Occurrence Data." National Academies of Sciences, Engineering, and Medicine. 2022. Review of Fate, Exposure, and Effects of Sunscreens in Aquatic Environments and Implications for Sunscreen Usage and Human Health. Washington, DC: The National Academies Press. doi: 10.17226/26381.
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Suggested Citation: "Appendix C: UV Filter Water and Sediment Occurrence Data." National Academies of Sciences, Engineering, and Medicine. 2022. Review of Fate, Exposure, and Effects of Sunscreens in Aquatic Environments and Implications for Sunscreen Usage and Human Health. Washington, DC: The National Academies Press. doi: 10.17226/26381.
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Suggested Citation: "Appendix C: UV Filter Water and Sediment Occurrence Data." National Academies of Sciences, Engineering, and Medicine. 2022. Review of Fate, Exposure, and Effects of Sunscreens in Aquatic Environments and Implications for Sunscreen Usage and Human Health. Washington, DC: The National Academies Press. doi: 10.17226/26381.
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Suggested Citation: "Appendix C: UV Filter Water and Sediment Occurrence Data." National Academies of Sciences, Engineering, and Medicine. 2022. Review of Fate, Exposure, and Effects of Sunscreens in Aquatic Environments and Implications for Sunscreen Usage and Human Health. Washington, DC: The National Academies Press. doi: 10.17226/26381.
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Suggested Citation: "Appendix C: UV Filter Water and Sediment Occurrence Data." National Academies of Sciences, Engineering, and Medicine. 2022. Review of Fate, Exposure, and Effects of Sunscreens in Aquatic Environments and Implications for Sunscreen Usage and Human Health. Washington, DC: The National Academies Press. doi: 10.17226/26381.
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Suggested Citation: "Appendix C: UV Filter Water and Sediment Occurrence Data." National Academies of Sciences, Engineering, and Medicine. 2022. Review of Fate, Exposure, and Effects of Sunscreens in Aquatic Environments and Implications for Sunscreen Usage and Human Health. Washington, DC: The National Academies Press. doi: 10.17226/26381.
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Suggested Citation: "Appendix C: UV Filter Water and Sediment Occurrence Data." National Academies of Sciences, Engineering, and Medicine. 2022. Review of Fate, Exposure, and Effects of Sunscreens in Aquatic Environments and Implications for Sunscreen Usage and Human Health. Washington, DC: The National Academies Press. doi: 10.17226/26381.
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Suggested Citation: "Appendix C: UV Filter Water and Sediment Occurrence Data." National Academies of Sciences, Engineering, and Medicine. 2022. Review of Fate, Exposure, and Effects of Sunscreens in Aquatic Environments and Implications for Sunscreen Usage and Human Health. Washington, DC: The National Academies Press. doi: 10.17226/26381.
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Suggested Citation: "Appendix C: UV Filter Water and Sediment Occurrence Data." National Academies of Sciences, Engineering, and Medicine. 2022. Review of Fate, Exposure, and Effects of Sunscreens in Aquatic Environments and Implications for Sunscreen Usage and Human Health. Washington, DC: The National Academies Press. doi: 10.17226/26381.
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Suggested Citation: "Appendix C: UV Filter Water and Sediment Occurrence Data." National Academies of Sciences, Engineering, and Medicine. 2022. Review of Fate, Exposure, and Effects of Sunscreens in Aquatic Environments and Implications for Sunscreen Usage and Human Health. Washington, DC: The National Academies Press. doi: 10.17226/26381.
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Suggested Citation: "Appendix C: UV Filter Water and Sediment Occurrence Data." National Academies of Sciences, Engineering, and Medicine. 2022. Review of Fate, Exposure, and Effects of Sunscreens in Aquatic Environments and Implications for Sunscreen Usage and Human Health. Washington, DC: The National Academies Press. doi: 10.17226/26381.
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Suggested Citation: "Appendix C: UV Filter Water and Sediment Occurrence Data." National Academies of Sciences, Engineering, and Medicine. 2022. Review of Fate, Exposure, and Effects of Sunscreens in Aquatic Environments and Implications for Sunscreen Usage and Human Health. Washington, DC: The National Academies Press. doi: 10.17226/26381.
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Suggested Citation: "Appendix C: UV Filter Water and Sediment Occurrence Data." National Academies of Sciences, Engineering, and Medicine. 2022. Review of Fate, Exposure, and Effects of Sunscreens in Aquatic Environments and Implications for Sunscreen Usage and Human Health. Washington, DC: The National Academies Press. doi: 10.17226/26381.
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Suggested Citation: "Appendix C: UV Filter Water and Sediment Occurrence Data." National Academies of Sciences, Engineering, and Medicine. 2022. Review of Fate, Exposure, and Effects of Sunscreens in Aquatic Environments and Implications for Sunscreen Usage and Human Health. Washington, DC: The National Academies Press. doi: 10.17226/26381.
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Suggested Citation: "Appendix C: UV Filter Water and Sediment Occurrence Data." National Academies of Sciences, Engineering, and Medicine. 2022. Review of Fate, Exposure, and Effects of Sunscreens in Aquatic Environments and Implications for Sunscreen Usage and Human Health. Washington, DC: The National Academies Press. doi: 10.17226/26381.
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Suggested Citation: "Appendix C: UV Filter Water and Sediment Occurrence Data." National Academies of Sciences, Engineering, and Medicine. 2022. Review of Fate, Exposure, and Effects of Sunscreens in Aquatic Environments and Implications for Sunscreen Usage and Human Health. Washington, DC: The National Academies Press. doi: 10.17226/26381.
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Suggested Citation: "Appendix C: UV Filter Water and Sediment Occurrence Data." National Academies of Sciences, Engineering, and Medicine. 2022. Review of Fate, Exposure, and Effects of Sunscreens in Aquatic Environments and Implications for Sunscreen Usage and Human Health. Washington, DC: The National Academies Press. doi: 10.17226/26381.
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Suggested Citation: "Appendix C: UV Filter Water and Sediment Occurrence Data." National Academies of Sciences, Engineering, and Medicine. 2022. Review of Fate, Exposure, and Effects of Sunscreens in Aquatic Environments and Implications for Sunscreen Usage and Human Health. Washington, DC: The National Academies Press. doi: 10.17226/26381.
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Suggested Citation: "Appendix C: UV Filter Water and Sediment Occurrence Data." National Academies of Sciences, Engineering, and Medicine. 2022. Review of Fate, Exposure, and Effects of Sunscreens in Aquatic Environments and Implications for Sunscreen Usage and Human Health. Washington, DC: The National Academies Press. doi: 10.17226/26381.
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Suggested Citation: "Appendix C: UV Filter Water and Sediment Occurrence Data." National Academies of Sciences, Engineering, and Medicine. 2022. Review of Fate, Exposure, and Effects of Sunscreens in Aquatic Environments and Implications for Sunscreen Usage and Human Health. Washington, DC: The National Academies Press. doi: 10.17226/26381.
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Suggested Citation: "Appendix C: UV Filter Water and Sediment Occurrence Data." National Academies of Sciences, Engineering, and Medicine. 2022. Review of Fate, Exposure, and Effects of Sunscreens in Aquatic Environments and Implications for Sunscreen Usage and Human Health. Washington, DC: The National Academies Press. doi: 10.17226/26381.
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Suggested Citation: "Appendix C: UV Filter Water and Sediment Occurrence Data." National Academies of Sciences, Engineering, and Medicine. 2022. Review of Fate, Exposure, and Effects of Sunscreens in Aquatic Environments and Implications for Sunscreen Usage and Human Health. Washington, DC: The National Academies Press. doi: 10.17226/26381.
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Suggested Citation: "Appendix C: UV Filter Water and Sediment Occurrence Data." National Academies of Sciences, Engineering, and Medicine. 2022. Review of Fate, Exposure, and Effects of Sunscreens in Aquatic Environments and Implications for Sunscreen Usage and Human Health. Washington, DC: The National Academies Press. doi: 10.17226/26381.
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Suggested Citation: "Appendix C: UV Filter Water and Sediment Occurrence Data." National Academies of Sciences, Engineering, and Medicine. 2022. Review of Fate, Exposure, and Effects of Sunscreens in Aquatic Environments and Implications for Sunscreen Usage and Human Health. Washington, DC: The National Academies Press. doi: 10.17226/26381.
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Suggested Citation: "Appendix C: UV Filter Water and Sediment Occurrence Data." National Academies of Sciences, Engineering, and Medicine. 2022. Review of Fate, Exposure, and Effects of Sunscreens in Aquatic Environments and Implications for Sunscreen Usage and Human Health. Washington, DC: The National Academies Press. doi: 10.17226/26381.
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Suggested Citation: "Appendix C: UV Filter Water and Sediment Occurrence Data." National Academies of Sciences, Engineering, and Medicine. 2022. Review of Fate, Exposure, and Effects of Sunscreens in Aquatic Environments and Implications for Sunscreen Usage and Human Health. Washington, DC: The National Academies Press. doi: 10.17226/26381.
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Suggested Citation: "Appendix C: UV Filter Water and Sediment Occurrence Data." National Academies of Sciences, Engineering, and Medicine. 2022. Review of Fate, Exposure, and Effects of Sunscreens in Aquatic Environments and Implications for Sunscreen Usage and Human Health. Washington, DC: The National Academies Press. doi: 10.17226/26381.
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Suggested Citation: "Appendix C: UV Filter Water and Sediment Occurrence Data." National Academies of Sciences, Engineering, and Medicine. 2022. Review of Fate, Exposure, and Effects of Sunscreens in Aquatic Environments and Implications for Sunscreen Usage and Human Health. Washington, DC: The National Academies Press. doi: 10.17226/26381.
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Suggested Citation: "Appendix C: UV Filter Water and Sediment Occurrence Data." National Academies of Sciences, Engineering, and Medicine. 2022. Review of Fate, Exposure, and Effects of Sunscreens in Aquatic Environments and Implications for Sunscreen Usage and Human Health. Washington, DC: The National Academies Press. doi: 10.17226/26381.
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Suggested Citation: "Appendix C: UV Filter Water and Sediment Occurrence Data." National Academies of Sciences, Engineering, and Medicine. 2022. Review of Fate, Exposure, and Effects of Sunscreens in Aquatic Environments and Implications for Sunscreen Usage and Human Health. Washington, DC: The National Academies Press. doi: 10.17226/26381.
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Next Chapter: Appendix D: Supplementary Information for Bioaccumulation
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