Land-Use-Based Sources and Trends of Dissolved pPBDEs and PAHs in an Urbanized Watershed Using Assive Polyethylene Samplers

Authors

Wenlu Zhao
Minggang Cai
Dave Adelman, University of Rhode IslandFollow
Mohammed Khairy, University of Rhode Island
Pete August, University of Rhode IslandFollow
Rainer Lohmann, University of Rhode IslandFollow

Document Type

Article

Date of Original Version

3-29-2018

Department

Oceanography

Abstract

Narragansett Bay is a temperate estuary on the Atlantic coast of Rhode Island in the north-eastern United States, which receives organic pollutants from urban and industrial activities in its watershed, though detailed knowledge on sources and fluxes is missing. Twenty-four polyethylene passive samplers were deployed in the surface water of the watershed around Narragansett Bay during June-July of 2014, to examine the spatial variability and possible sources of priority pollutants, namely dissolved polycyclic aromatic hydrocarbons (PAHs) and polybrominated diphenyl ethers (PBDEs). Dissolved ∑₂₂PAH concentrations ranged from 3.6 to 340 ng L^-1, and from 2.9 to 220 pg L^-1 for ∑₁₂PBDE. The spatial variability of the concentrations was correlated to land use pattern and population distribution, in particular with human activities within 2 km of sampling sites. River discharges derived from the concentrations of PAHs and PBDEs measured here were 10-20 times greater than their previously measured concentrations in the open waters of Narragansett Bay. These results imply that river waters are the main source of PAHs and PDBEs to the Bay and that major sink terms (e.g., sedimentation, degradation) affect their concentrations in the estuary. Predicted PAH and PBDE toxicity based on dissolved concentrations did not exceed 1 toxic unit, suggested that no toxicity occurred at the sampling sites.

Citation/Publisher Attribution

Zhao, W., Cai, M., Adelman, D., Khairy, M., August, P., & Lohmann, R. (2018). Land-use-based sources and trends of dissolved PBDEs and PAHs in an urbanized watershed using passive polyethylene samplers. Environmental Pollution, 238, 573-580. doi:10.1016/j.envpol.2018.02.057