Abstract

Seasonal hypoxia is a characteristic feature of the Chesapeake Bay due to anthropogenic nutrient input from agriculture and urbanization throughout the watershed. Although coordinated management efforts since 1985 have reduced nutrient inputs to the Bay, oxygen concentrations at depth in the summer still frequently fail to meet water quality standards that have been set to protect critical estuarine living resources. To quantify the impact of watershed nitrogen reductions on Bay hypoxia during a recent period including both average discharge and extremely wet years (2016–2019), this study employed both statistical and three-dimensional (3-D) numerical modeling analyses. Numerical model results suggest that if the nitrogen reductions since 1985 had not occurred, annual hypoxic volumes (O2 < 3 mg L−1) would have been ~50–120% greater during the average discharge years of 2016–2017 and ~20–50% greater during the wet years of 2018–2019. The effect was even greater for O2 < 1 mg L−1, where annual volumes would have been ~80–280% greater in 2016–2017 and ~30–100% greater in 2018–2019. These results were supported by statistical analysis of empirical data, though the magnitude of improvement due to nitrogen reductions was greater in the numerical modeling results than in the statistical analysis. This discrepancy is largely accounted for by warming in the Bay that has exacerbated hypoxia and offset roughly 6–34% of the improvement from nitrogen reductions. Although these results may reassure policymakers and stakeholders that their efforts to reduce hypoxia have improved ecosystem health in the Bay, they also indicate that greater reductions are needed to counteract the ever-increasing impacts of climate change.

Highlights

  • Hypoxia resulting from anthropogenic eutrophication has become one of the greatest threats to the health of estuarine and coastal ecosystems worldwide due to its ability to degrade habitat, decrease biodiversity, and alter food-web interactions (Diaz and Rosenberg, 2008)

  • Results from sensitivity experiments showed that the greatest impact of nutrient reductions generally occurs at the southern end of where hypoxia develops in the Bay, somewhere between the Patuxent and Rappahannock Rivers (~100–200 km from the Bay mouth), irrespective of year and oxygen threshold (Fig. 7)

  • This study has demonstrated that nutrient reductions from 1985 to 2019 have made the Chesapeake Bay more resilient to warming atmospheric temperatures and high discharge years by preventing additional hypoxia from developing

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Summary

Introduction

Hypoxia resulting from anthropogenic eutrophication has become one of the greatest threats to the health of estuarine and coastal ecosystems worldwide due to its ability to degrade habitat, decrease biodiversity, and alter food-web interactions (Diaz and Rosenberg, 2008). The Bay is naturally a highly productive estuary that receives a large flux of nutrients from terrestrial sources due to its extensive watershed that spans six states and the District of Columbia, encompassing 164,200 km (Kemp et al, 2005) The magnitude of this nutrient flux varies in response to changes in land-use within the watershed, the most notable of which occurred during the European colonization of the area in the 17th century, and the post-World War II increase in fertilizer usage throughout the watershed. Through analysis of both observational data (Hagy et al, 2004; Kemp et al, 2005; Officer et al, 1984) and proxies within sediment cores (Cooper and Brush, 1991, 1993), current low oxygen conditions within the Chesapeake Bay have been definitively attributed to anthropogenic eutrophication

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