Abstract

Abstract. Water masses can become undersaturated with oxygen when natural processes alone or in combination with anthropogenic processes produce enough organic carbon that is aerobically decomposed faster than the rate of oxygen re-aeration. The dominant natural processes usually involved are photosynthetic carbon production and microbial respiration. The re-supply rate is indirectly related to its isolation from the surface layer. Hypoxic water masses (<2 mg L−1, or approximately 30% saturation) can form, therefore, under "natural" conditions, and are more likely to occur in marine systems when the water residence time is extended, water exchange and ventilation are minimal, stratification occurs, and where carbon production and export to the bottom layer are relatively high. Hypoxia has occurred through geological time and naturally occurs in oxygen minimum zones, deep basins, eastern boundary upwelling systems, and fjords. Hypoxia development and continuation in many areas of the world's coastal ocean is accelerated by human activities, especially where nutrient loading increased in the Anthropocene. This higher loading set in motion a cascading set of events related to eutrophication. The formation of hypoxic areas has been exacerbated by any combination of interactions that increase primary production and accumulation of organic carbon leading to increased respiratory demand for oxygen below a seasonal or permanent pycnocline. Nutrient loading is likely to increase further as population growth and resource intensification rises, especially with increased dependency on crops using fertilizers, burning of fossil fuels, urbanization, and waste water generation. It is likely that the occurrence and persistence of hypoxia will be even more widespread and have more impacts than presently observed. Global climate change will further complicate the causative factors in both natural and human-caused hypoxia. The likelihood of strengthened stratification alone, from increased surface water temperature as the global climate warms, is sufficient to worsen hypoxia where it currently exists and facilitate its formation in additional waters. Increased precipitation that increases freshwater discharge and flux of nutrients will result in increased primary production in the receiving waters up to a point. The interplay of increased nutrients and stratification where they occur will aggravate and accelerate hypoxia. Changes in wind fields may expand oxygen minimum zones onto more continental shelf areas. On the other hand, not all regions will experience increased precipitation, some oceanic water temperatures may decrease as currents shift, and frequency and severity of tropical storms may increase and temporarily disrupt hypoxia more often. The consequences of global warming and climate change are effectively uncontrollable at least in the near term. On the other hand, the consequences of eutrophication-induced hypoxia can be reversed if long-term, broad-scale, and persistent efforts to reduce substantial nutrient loads are developed and implemented. In the face of globally expanding hypoxia, there is a need for water and resource managers to act now to reduce nutrient loads to maintain, at least, the current status.

Highlights

  • Over the past five to ten years, changes in the ocean’s dissolved oxygen content have become a focal point of oceanic research

  • The formation of hypoxic areas has been exacerbated by any combination of interactions that increase primary production and accumulation of organic carbon leading to increased respiratory demand for oxygen below a seasonal or permanent pycnocline

  • The ecosystems in which hypoxia occurs range from inshore estuaries, through the coastal ocean and into ocean waters, over depths of 1- to 2-m in estuaries to 600- to 700-m in the open ocean and vary in physiography, physical processes, organic and nutrient loading, and ecosystem structure

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Summary

Introduction

Over the past five to ten years, changes in the ocean’s dissolved oxygen content have become a focal point of oceanic research. Dıaz and Rosenberg (1995) noted that no other environmental variable of such ecological importance to estuarine and coastal marine ecosystems has changed so drastically, in such a short period of time They noted consistent trends of increasing severity in duration, intensity, or extent in areas where hypoxia has a long history, which were coincidental with an increase in human activities. The negative effects of hypoxia include loss of suitable and required habitat for many bottom-dwelling fishes and benthic fauna, habitat compression for pelagic fishes, direct mortality, increased predation, decreased food resources, altered trophic energy transfer, altered bioenergetics (physiological, development, growth, and reproductive abnormalities) and altered migration These result in reduced fisheries, including valuable finfishes and crustaceans (Jørgensen, 1980; Nissling and Vallin, 1996; Rabalais and Turner, 2001; Cheng et al, 2002; Eby and Crowder, 2002; Kodama et al, 2002; Wu, 2002; Wu et al, 2003; Baird et al, 2004; Breitburg et al, 2009). Hypoxic waters from OMZs and upwelling systems may impinge on coastal areas with similar affects as humaninduced hypoxia (Levin et al, 2009a)

Definitions and terminology
Oxygen minimum zones
Upwelling areas
Water column processes
Sedimentary processes
The Baltic Sea and Scandinavian waters
Mississippi River-influenced Gulf of Mexico
East China Sea
Northern Adriatic Sea
Chesapeake Bay
Northwestern shelf of the Black Sea
Tampa Bay
Baltic Sea
Mississippi River and northern Gulf of Mexico
Approaches and implications of nutrient reduction
10.1 Increases in eutrophication-driven hypoxia
10.2 Climate change and coastal waters
10.3 Oceanic waters
Findings
11 Conclusions
Full Text
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