Abstract

Deltas and estuaries built by the Mississippi/Atchafalaya River (MAR) in the United States and the Usumacinta/Grijalva River (UGR) in Mexico account for 80 percent of all Gulf of Mexico (GoM) coastal wetlands outside of Cuba. They rank first and second in freshwater discharge to the GoM and owe their natural resilience to a modular geomorphology that spreads risk across the coast-scape while providing ecosystem connectivity through shelf plumes that connect estuaries. Both river systems generate large plumes that strongly influence fisheries production over large areas of the northern and southern GoM continental shelves. Recent watershed process simulations (DLEM, MAPSS) driven by CMIP3 General Circulation Model (GCM) output indicate that the two systems face diverging futures, with the mean annual discharge of the MAR predicted to increase 11 to 63 percent, and that of the UGR to decline as much as 80 percent in the 21st century. MAR delta subsidence rates are the highest in North America, making it particularly susceptible to channel training interventions that have curtailed a natural propensity to shift course and deliver sediment to new areas, or to refurbish zones of high wetland loss. Undoing these restrictions in a controlled way has become the focus of a multi-billion-dollar effort to restore the MAR delta internally, while releasing fine-grained sediments trapped behind dams in the Great Plains has become an external goal. The UGR is, from an internal vulnerability standpoint, most threatened by land use changes that interfere with a deltaic architecture that is naturally resilient to sea level rise. This recognition has led to successful efforts in Mexico to protect still intact coastal systems against further anthropogenic impacts, as evidenced by establishment of the Centla Wetland Biosphere Preserve and the Terminos Lagoon Protected Area. The greatest threat to the UGR system, however, is an external one that will be imposed by the severe drying predicted for the entire Mesoamerican “climate change hot-spot”, a change that will necessitate much greater international involvement to protect threatened communities and lifeways as well as rare habitats and species.

Highlights

  • The Mississippi/Atchafalaya (MAR) and Usumacinta/Grijalva Rivers (UGR) rank first (18,000 m3 ̈ s1, 650 km3 ̈ year1 ) and second (4500 m3 ̈ s1, 140 km3 ̈ year1 ) in freshwater dischargeWater 2016, 8, 83; doi:10.3390/w8030083 www.mdpi.com/journal/water to[1,2].the Gulf of Mexico TheUGR flows into the throughGulf of Mexico (GoM)through the MexicanThe UGR flows [1,2].into the the Mexican states of Tabasco and states of Tabasco and Campeche (Figure 1)

  • The 75% reduction in fishing pressure since the late 1990s in areas areas influenced by the Mississippi/Atchafalaya River (MAR) plume reflects competition with low-cost farmed shrimp imported influenced by the MAR plume reflects competition with low-cost farmed shrimp imported mainly from mainly from Asian countries [33]

  • If theplume volume and seasonality of river how discharge primary will factors affectingby deltaic resiliency and shelf dynamics, projecting these are parameters be affected climate change and shelf to plume dynamics, how River these discharge parametershas will be affected by climatenot change is critical assessing futurethen deltaprojecting vulnerability

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Summary

Introduction

The Mississippi/Atchafalaya (MAR) and Usumacinta/Grijalva Rivers (UGR) rank first (18,000 m3 ̈ s1 , 650 km3 ̈ year1 ) and second (4500 m3 ̈ s1 , 140 km3 ̈ year1 ) in freshwater discharge. Coasts discharges on the northern (28 ̋ to 29 ̋ N) and southern (18 ̋ to 19 ̋ N) GoM coasts are temporally offset, occurring on the MAR from March to May coincident with snow melt and spring rains, while this is the dry season in the Bay of Campeche. Both systems are affected by hurricanes, most frequently in August and September, though the potential for large storm surges is far greater on the northern. The DLEM and MAPSS models have been calibrated against historic MAR and runoff for the 1901–2008 and 1950–2000 intervals, respectively [4,6]

Observed and estimatedindices indices of of shrimp shrimp trawling
Study Sites
Deltaic
Climate Change Effects on River Discharge
Synthesis
Mesoscale Circulation in the Gulf of Mexico
Plume Dynamics and Coastal Currents
Findings
Conclusions and Management Implications
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