Reconstitution studies of pesticides and surfactants exploring the cause of estrogenic activity observed in surface waters of the San Francisco Bay Delta.

To evaluate the potential role of endocrine disruption in the decline of pelagic fishes in the San Francisco Bay Delta of California, various surface water samples were collected, extracted, and found to elicit estrogenic activity in laboratory fish. Chemical analysis of the estrogenic samples indicated 2 pesticides (bifenthrin, diuron), 2 alkyphenols (AP), and mixtures of 2 types of alkyphenol polyethoxylates (APEOs). Evaluation of estrogenic activity was further characterized by in vitro bioassays using rainbow trout hepatocytes (Oncorhynchus mykiss) and in vivo studies with Japanese medaka (Oryzias latipes). In the in vitro bioassays, hepatocytes exposed to the pesticides alone or in combination with the AP/APEO mixtures at concentrations observed in surface waters failed to show estrogenic activity (induction of vitelloginin mRNA). In the in vivo bioassays, medaka exposed to individual pesticides or to AP/APEO alone did not have elevated VTG at ambient concentrations. However, when the pesticides were combined with AP/APEOs in the 7-day exposure a significant increase in VTG was observed. Exposure to a 5-fold higher concentration of the AP/APEO mixture alone also significantly induced VTG. In contrast to earlier studies with permethrin, biotransformation of bifenthrin to estrogenic metabolites was not observed in medaka liver microsomes and cytochrome P450 was not induced with AP/APEO treatment. These results showed that mixtures of pesticides with significantly different modes of action and AP/APEOs at environmentally relevant concentrations may be associated with estrogenic activity measured in water extracts and feral fish that have been shown to be in population decline in the San Francisco Bay Delta.

Fate and distribution of the octyl- and nonylphenol ethoxylates and some carboxylated transformation products in the Back River, Maryland.

The concentrations of nonylphenol (NP), octylphenol (OP), their ethoxylates (NP1-16EO and OP1-5EO respectively) and some of their carboxylated derivatives (NP1-2EC and OP1EC quantitatively; NP3-4EC and OP2EC qualitatively) were measured in water samples from the Back River, MD, a sub-estuary of the Chesapeake Bay that receives effluent from a large municipal wastewater treatment plant. The most abundant of the alkylphenolic compounds (APEs) were the carboxylates (APECs, >95% of the APE-related compounds), followed by NP in September and October, and NP1-2EO in March. Ratios of the different compounds' concentrations provide evidence for the season dependency of two different degradation pathways. NP concentrations found in this study, 0.087-0.69 microg L(-1), were below acute toxicity thresholds, and below US EPA water quality criteria; although in March, concentrations were close to 40% of the chronic exposure limit for saltwater, 1.7 microg L(-1). A simple steady-state model of the Back River suggested that total NPE concentrations in the estuary varied in accordance with concentrations in the wastewater treatment plant effluent, especially in the case of the APECs. This model also suggested that in the fall sampling events, when rain occurred, APEOs present in particulate matter might have originated in the river's tributaries rather than the treatment plant.