title: Effects of biologically-active chemical mixtures on fish in a wastewater-impacted urban stream.
abstract: Stream flow in urban aquatic ecosystems often is maintained by water-reclamation plant (WRP) effluents that contain mixtures of natural and anthropogenic chemicals that persist through the treatment processes. In effluent-impacted streams, aquatic organisms such as fish are continuously exposed to biologically-active chemicals throughout their life cycles. The North Shore Channel of the Chicago River (Chicago, Illinois) is part of an urban ecosystem in which >80% of the annual flow consists of effluent from the North Side WRP. In this study, multiple samplings of the effluent and stream water were conducted and fish (largemouth bass and carp) were collected on 2 occasions from the North Shore Channel. Fish also were collected once from the Outer Chicago Harbor in Lake Michigan, a reference site not impacted by WRP discharges. Over 100 organic chemicals with differing behaviors and biological effects were measured, and 23 compounds were detected in all of the water samples analyzed. The most frequently detected and highest concentration (>100μg/L) compounds were ethylenediaminetetraacetic acid and 4-nonylphenolmono-to-tetraethoxycarboxylic acids. Other biologically-active chemicals including bisphenol A, 4-nonylphenol, 4-nonylphenolmono-to-tetraethoxylates, 4-tert-octylphenol, and 4-tert-octylphenolmono-to-tetraethoxylates were detected at lower concentrations (<5μg/L). The biogenic steroidal hormones 17β-estradiol, estrone, testosterone, 4-androstene-3,17-dione, and cis-androsterone were detected at even lower concentrations (<0.005μg/L). There were slight differences in concentrations between the North Side WRP effluent and the North Shore Channel, indicating minimal in-stream attenuation. Fish populations are continuously exposed to mixtures of biologically-active chemicals because of the relative persistency of the chemicals with respect to stream hydraulic residence time, and the lack of a fresh water source for dilution. The majority of male fish exhibited vitellogenin induction, a physiological response consistent with exposure to estrogenic compounds. Tissue-level signs of reproductive disruption, such as ovatestis, were not observed.
authors.affiliation: U.S. Geological Survey, 3215 Marine Street, Boulder, CO 80303, USA. lbbarber@usgs.gov
authors.forename: Larry B
authors.initials: LB
authors.lastname: Barber
authors.forename: Gregory K
authors.initials: GK
authors.lastname: Brown
authors.forename: Todd G
authors.initials: TG
authors.lastname: Nettesheim
authors.forename: Elizabeth W
authors.initials: EW
authors.lastname: Murphy
authors.forename: Stephen E
authors.initials: SE
authors.lastname: Bartell
authors.forename: Heiko L
authors.initials: HL
authors.lastname: Schoenfuss
mesh_terms: D000818:Animals; D001492:Bass / Q000378:metabolism*; D002347:Carps / Q000378:metabolism*; D002641:Chicago; D004781:Environmental Exposure; D012739:Gonadal Steroid Hormones / Q000032:analysis; D008297:Male; D009930:Organic Chemicals / Q000032:analysis*; D045483:Rivers; D014818:Vitellogenesis / Q000187:drug effects; D014874:Water Pollutants, Chemical / Q000032:analysis* / Q000633:toxicity*
chemical_list: D012739:Gonadal Steroid Hormones; D009930:Organic Chemicals; D014874:Water Pollutants, Chemical