Jocelyn Hemming | Search USGS

USGS2025

Comparative toxicity of aircraft deicers, runway deicers, and road salt in winter airport runoff

Aircraft deicer and anti-icer formulations and airfield pavement deicer formulations are commonly used at airports that experience freezing precipitation. In addition, road salt is often applied in urban areas surrounding airports. This mixture of deicers in receiving streams can be toxic to aquatic organisms. A 17-year study of deicers and toxicity in runoff samples from sites in and near Milwaukee Mitchell International Airport included bioassay testing of Ceriodaphnia dubia , Pimephales promelas , Raphidocelis subcapitata , and Aliivibrio fischeri concurrently with quantification of freezing-point depressants that represent presence of the various deicers. Propylene glycol was monitored to represent aircraft deicers and anti-icers, acetate and formate were monitored to represent airfield pavement deicers, and chloride was monitored to represent road salt. Toxicity endpoints (e.g., lethal concentrations and inhibitive concentrations) were compiled for 19 airport deicer products and sodium chloride. Comparison of freezing-point depressant concentrations with toxicity endpoints indicated that propylene glycol, acetate, and chloride exceeded endpoint concentrations in multiple samples: more than 70% of 492 runoff samples exceeded at least one endpoint concentration with exceedances of propylene glycol and acetate-based deicer endpoints as well as road salt endpoints. Validation of these results were observed with measured toxic effects on C. dubia , P. promelas , and R. subcapitata in bioassays conducted on undiluted samples: samples with multiple deicers exceeding endpoint thresholds had greater toxicity than samples with individual deicer endpoint exceedances, and samples with no endpoint exceedances typically exhibited less toxicity than samples with only one endpoint exceedance. A comparison of additivity of toxicity quotients with bioassay results fit a log-logistic regression curve, indicating that the condition of tested organisms degraded with increasing deicer presence. These findings suggest that concurrent reduction of runoff from aircraft, airfield pavement, and road salt deicers will be needed to eliminate aquatic toxicity in adjacent watersheds.

Wisconsin↗

USGS2014

Spatiotemporal variations in estrogenicity, hormones, and endocrine-disrupting compounds in influents and effluents of selected wastewater-treatment plants and receiving streams in New York, 2008-09

Endocrine-disrupting compounds (EDCs) in wastewater effluents have been linked to changes in sex ratios, intersex (in males), behavioral modifications, and developmental abnormalities in aquatic organisms. Yet efforts to identify and regulate specific EDCs in complex mixtures are problematic because little is known about the estrogen activity (estrogenicity) levels of many common and emerging contaminants. The potential effects of EDCs on the water quality and health of biota in streams of the New York City water supply is especially worrisome because more than 150 wastewater-treatment plants (WWTPs) are permitted to discharge effluents into surface waters and groundwaters of watersheds that provide potable water to more than 9 million people. In 2008, the U.S. Geological Survey (USGS), the New York State Department of Environmental Conservation (NYSDEC), New York State Department of Health (NYSDOH), and New York City Department of Environmental Protection (NYCDEP) began a pilot study to increase the understanding of estrogenicity and EDCs in effluents and receiving streams mainly in southeastern New York. The primary goals of this study were to document and assess the spatial and temporal variability of estrogenicity levels; the effectiveness of various treatment-plant types to remove estrogenicity; the concentrations of hormones, EDCs, and pharmaceuticals, personal care products (PPCPs); and the relations between estrogenicity and concentrations of hormones, EDCs, and PPCPs. The levels of estrogenicity and selected hormones, non-hormone EDCs, and PPCPs were characterized in samples collected seasonally in effluents from 7 WWTPs, once or twice in effluents from 34 WWTPs, and once in influents to 6 WWTPs. Estrogenicity was quantified, as estradiol equivalents, using both the biological e-screen assay and a chemical model. Results generally show that (1) estrogenicity levels in effluents varied spatially and seasonally, (2) a wide range of known and unknown EDCs were present in both WWTP effluents and receiving streams, (3) some effluents may be important sources of estrogenicity in weakly diluted streams, (4) measured levels of biological estrogenicity were often higher than estimated levels of chemical estrogenicity, and (5) the type of treatment had a large effect on the removal efficacy, and consequently, the estrogenicity levels observed in treated effluents.

New York↗