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. 2024 May 21;31(26):37907–37922. doi: 10.1007/s11356-024-33713-z

Table 4.

Estrogen concentrations (E1, 17α-E, 17β-E2, and E3) in ng/dm3 in the water solutions (based on Adeel et al. 2017)

Sample Estrone (E1) 17α-estradiol (17α-E2) 17β-estradiol (17β-E2) Estriol (E3) Reference
Slurry
  In swine pit 5900–150,000 4000–84,000 1800–49,000 nd (Li et al. 2010)
  In dairy pit 2500–80,000 2000–5000 800–27,000 nd (Li et al. 2010)
Swine
  Farm effluent 5200–5400 650–680 1000–1500 2200–3000 (Franks 2006)
  Manure 70.0 175 15 nd (Rodriguez-Navas et al. 2013)
  Manure leachate 68.1 2.5 nd nd (Kjær et al. 2007)
Dairy farm wastewater 370–2356 1750–3270 351–957 nd (Li et al. 2010)
Lagoon pond 650 nd nd nd (Rodriguez-Navas et al. 2013)
Sow urine 416–490 nd 85–97 127–193 (Zhang et al. 2014)
Grazing land water 78 31 18 nd (Kolodziej and Sedlak 2007)
1 m deep groundwater 68.1 nd 2.5 nd (Li et al. 2010)
Surface waters 0.7 nd nd nd (Bolong et al. 2009)
0.1–3.4 nd nd nd (Włodarczyk-Makuła 2016)
Drinking water 0.4 nd 0.3–2.1 nd (Bolong et al. 2009)
STP/effluent 12–196 6.4–12.6 6.2–42.2 nd (Pal et al. 2010)

*nd no data