Lin Hsing-Juh, Shao Kwang-Tsao, Jan Rong-Quen, Hsieh Hwey-Lian, Chen Chang-Po, Hsieh Li-Yung, Hsiao Yi-Ting
Department of Life Sciences, National Chung Hsing University, Taichung 402, Taiwan, ROC.
Mar Pollut Bull. 2007 Nov;54(11):1789-800. doi: 10.1016/j.marpolbul.2007.07.008. Epub 2007 Sep 10.
The estuary of the Danshuei River, a hypoxic subtropical estuary, receives a high rate of untreated sewage effluent. The Ecopath with Ecosim software system was used to construct a mass-balanced trophic model for the estuary, and network analysis was used to characterize the structure and matter flow in the food web. The estuary model was comprised of 16 compartments, and the trophic levels varied from 1.0 for primary producers and detritus to 3.0 for carnivorous and piscivorous fishes. The large organic nutrient loading from the upper reaches has resulted in detritivory being more important than herbivory in the food web. The food-chain length of the estuary was relatively short when compared with other tropical/subtropical coastal systems. The shortness of food-chain length in the estuary could be attributed to the low biomass of the top predators. Consequently, the trophic efficiencies declined sharply for higher trophic levels due to low fractions of flows to the top predators and then high fractions to detritus. The low biomass of the top predators in the estuary was likely subject to over-exploitation and/or hypoxic water. Summation of individual rate measurements for primary production and respiration yielded an estimate of -1791 g WW m(-2) year(-1), or -95 g C m(-2) year(-1), suggesting a heterotrophic ecosystem, which implies that more organic matter was consumed than was produced in the estuary.
淡水河河口是一个亚热带缺氧河口,接纳了大量未经处理的污水。利用Ecopath with Ecosim软件系统构建了该河口的质量平衡营养模型,并采用网络分析来描述食物网的结构和物质流动。河口模型由16个功能组组成,营养级从初级生产者和碎屑的1.0级到肉食性和食鱼性鱼类的3.0级不等。上游大量的有机养分负荷导致碎屑食性在食物网中比草食性更为重要。与其他热带/亚热带沿海系统相比,该河口的食物链长度相对较短。河口食物链长度较短可能归因于顶级捕食者的生物量较低。因此,由于流向顶级捕食者的流量比例较低,而流向碎屑的比例较高,较高营养级的营养效率急剧下降。河口顶级捕食者的低生物量可能受到过度捕捞和/或缺氧水体的影响。初级生产和呼吸的个体速率测量总和得出估计值为-1791 g WW m(-2) 年(-1),或-95 g C m(-2) 年(-1),表明该生态系统为异养型,这意味着河口消耗的有机物质多于产生的有机物质。