Department of Oceanography, Texas A&M University, College Station, Texas 77843-3146, USA.
Sci Total Environ. 2010 Mar 1;408(7):1471-84. doi: 10.1016/j.scitotenv.2009.11.047. Epub 2010 Jan 25.
The Mississippi River is one of the world's 10 largest rivers, with average freshwater discharge into the northern Gulf of Mexico (GOM) of 380km(3) year(-1). In the northern GOM, anthropogenic nitrogen is primarily derived from agricultural fertilizer and delivered via the Mississippi River. The general consensus is that hypoxia in the northern Gulf of Mexico is caused primarily by algal production stimulated by excess nitrogen delivered from the Mississippi-Atchafalaya River Basin and seasonal vertical stratification of incoming stream flow and Gulf waters, which restricts replenishment of oxygen from the atmosphere. In this paper, we review the controversial aspects of the largely nutrient-centric view of the hypoxic region, and introduce the role of non-riverine organic matter inputs as other oxygen-consuming mechanisms. Similarly, we discuss non-nutrient physically-controlled impacts of freshwater stratification as an alternative mechanism for controlling in part, the seasonality of hypoxia. We then explore why hypoxia in this dynamic river-dominated margin (RiOMar) is not comparable to many of the other traditional estuarine systems (e.g., Chesapeake Bay, Baltic Sea, and Long Island Sound). The presence of mobile muds and the proximity of the Mississippi Canyon are discussed as possible reasons for the amelioration of hypoxia (e.g., healthy fisheries) in this region. The most recent prediction of hypoxia area for 2009, using the current nutrient-centric models, failed due to the limited scope of these simple models and the complexity of this system. Predictive models should not be the main driver for management decisions. We postulate that a better management plan for this region can only be reached through a more comprehensive understanding of this RiOMar system-not just more information on river fluxes (e.g., nutrients) and coastal hypoxia monitoring programs.
密西西比河是世界十大河流之一,其向墨西哥湾北部(GOM)的平均淡水排放量为 380km³ 年-1。在墨西哥湾北部,人为氮主要来自农业肥料,并通过密西西比河输送。人们普遍认为,墨西哥湾北部的缺氧主要是由密西西比-阿查法拉亚河流域过量氮输送刺激的藻类生产引起的,以及入流和海湾水的季节性垂直分层,这限制了大气中氧气的补充。在本文中,我们回顾了关于缺氧区主要以营养为中心的观点的争议方面,并介绍了非河流有机物输入作为其他耗氧机制的作用。同样,我们讨论了淡水分层的非营养物理控制影响,作为控制缺氧部分季节性的替代机制。然后,我们探讨了为什么这个动态的河流主导边缘(RiOMar)的缺氧与许多其他传统河口系统(例如切萨皮克湾、波罗的海和长岛海峡)不同。我们讨论了移动的淤泥的存在和密西西比峡谷的接近程度,作为该地区缺氧缓解(例如健康的渔业)的可能原因。由于这些简单模型的范围有限以及该系统的复杂性,使用当前以营养为中心的模型对 2009 年缺氧区的最新预测失败了。预测模型不应成为管理决策的主要驱动因素。我们假设,只有通过对这个 RiOMar 系统有更全面的了解,而不仅仅是更多关于河流通量(例如营养物)和沿海缺氧监测计划的信息,才能为该地区制定更好的管理计划。