Environmental exposure assessment of ethinyl estradiol (EE) from a combined hormonal vaginal contraceptive ring after disposal; leaching from landfills.

In this study an environmental exposure assessment and experiments were carried out to identify the leaching potential of ethinyl estradiol (EE) present in a vaginal contraceptive (NuvaRing) when disposed of in landfills. Landfill material and a sandy soil were used to investigate the mobility of EE. Log K(oc) values determined in the range of 3 to 4 indicate that EE does not have a high mobility in landfills and soils. Column experiments were used to estimate that it takes approximately 40 years before EE leaches from a column of 1 m of landfill material or sandy soil. This column experiment, which was performed with an EE concentration based on worst-case assumptions, demonstrates that the emission of EE from landfills is negligible. Sandy soils below landfills also act as a strong sorbent of EE, thereby further reducing the potential for groundwater contamination.

Assessment of the biodegradability of dialkyldimethylammonium salts in flow through systems.

A bacterium capable of utilizing the alkyl chains of didecyldimethylammonium salt was isolated from activated sludge. In addition, the isolate also utilized didodecyldimethylammonium salt, ditetradecyldimethylammonium salt and alkyltrimethylammonium salts (C10 to C18) as sole source of carbon and energy. The broad substrate with respect to the alkyl chain length was also demonstrated with oxidation rates of various quaternary ammonium salts by didecyldimethylammonium chloride-grown cells. The oxidation rate decreased with increasing alkyl chain lengths. The main factor impeding the biodegradation of dialkyldimethylammonium salts with long alkyl chains is probably the low bioavailability of water-insoluble chemicals. The biodegradability of dialkyldimethylammonium salts was therefore determined in flow-through columns at concentrations below their aqueous solubility. Dialkyldimethylammonium salts adsorbed on silica gel particles packed in flow-through columns were immediately metabolized by the isolate when dissolved. Microorganisms present in river water pumped through a sterile column degraded dissolved dicocodimethylammonium salts within a week.