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Life Cycle of Oil and Gas Fields in the Mississippi River Delta: A Review

Department of Oceanography and Coastal Sciences, Louisiana State University, Baton Rouge, LA 70803, USA
Department of Earth, Environmental and Planetary Science, Rice University, Houston, TX 77005, USA
Department of Geological Sciences, Chungnam National University, Daejeon 34134, Korea
Comite Resources, Inc., P.O. Box 66596, Baton Rouge, LA 70896, USA
Charles Norman & Associates, P.O. Box 5715, Lake Charles LA 70606, USA
Authors to whom correspondence should be addressed.
Water 2020, 12(5), 1492;
Received: 20 April 2020 / Revised: 18 May 2020 / Accepted: 20 May 2020 / Published: 23 May 2020
Oil and gas (O&G) activity has been pervasive in the Mississippi River Delta (MRD). Here we review the life cycle of O&G fields in the MRD focusing on the production history and resulting environmental impacts and show how cumulative impacts affect coastal ecosystems. Individual fields can last 40–60 years and most wells are in the final stages of production. Production increased rapidly reaching a peak around 1970 and then declined. Produced water lagged O&G and was generally higher during declining O&G production, making up about 70% of total liquids. Much of the wetland loss in the delta is associated with O&G activities. These have contributed in three major ways to wetland loss including alteration of surface hydrology, induced subsidence due to fluids removal and fault activation, and toxic stress due to spilled oil and produced water. Changes in surface hydrology are related to canal dredging and spoil placement. As canal density increases, the density of natural channels decreases. Interconnected canal networks often lead to saltwater intrusion. Spoil banks block natural overland flow affecting exchange of water, sediments, chemicals, and organisms. Lower wetland productivity and reduced sediment input leads to enhanced surficial subsidence. Spoil banks are not permanent but subside and compact over time and many spoil banks no longer have subaerial expression. Fluid withdrawal from O&G formations leads to induced subsidence and fault activation. Formation pore pressure decreases, which lowers the lateral confining stress acting in the formation due to poroelastic coupling between pore pressure and stress. This promotes normal faulting in an extensional geological environment like the MRD, which causes surface subsidence in the vicinity of the faults. Induced reservoir compaction results in a reduction of reservoir thickness. Induced subsidence occurs in two phases especially when production rate is high. The first phase is compaction of the reservoir itself while the second phase is caused by a slow drainage of pore pressure in bounding shales that induces time-delayed subsidence associated with shale compaction. This second phase can continue for decades, even after most O&G has been produced, resulting in subsidence over much of an oil field that can be greater than surface subsidence due to altered hydrology. Produced water is water brought to the surface during O&G extraction and an estimated 2 million barrels per day were discharged into Louisiana coastal wetlands and waters from nearly 700 sites. This water is a mixture of either liquid or gaseous hydrocarbons, high salinity (up to 300 ppt) water, dissolved and suspended solids such as sand or silt, and injected fluids and additives associated with exploration and production activities and it is toxic to many estuarine organisms including vegetation and fauna. Spilled oil has lethal and sub-lethal effects on a wide range of estuarine organisms. The cumulative effect of alterations in surface hydrology, induced subsidence, and toxins interact such that overall impacts are enhanced. Restoration of coastal wetlands degraded by O&G activities should be informed by these impacts. View Full-Text
Keywords: oil and gas production; produced water; oil and gas wetland impacts; induced subsidence; wetland restoration oil and gas production; produced water; oil and gas wetland impacts; induced subsidence; wetland restoration
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MDPI and ACS Style

Day, J.W.; Clark, H.C.; Chang, C.; Hunter, R.; Norman, C.R. Life Cycle of Oil and Gas Fields in the Mississippi River Delta: A Review. Water 2020, 12, 1492.

AMA Style

Day JW, Clark HC, Chang C, Hunter R, Norman CR. Life Cycle of Oil and Gas Fields in the Mississippi River Delta: A Review. Water. 2020; 12(5):1492.

Chicago/Turabian Style

Day, John W.; Clark, H. C.; Chang, Chandong; Hunter, Rachael; Norman, Charles R. 2020. "Life Cycle of Oil and Gas Fields in the Mississippi River Delta: A Review" Water 12, no. 5: 1492.

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