Thorp James H, Delong Michael D, Greenwood Kim S, Casper Andrew F
Department of Biology, University of Louisville, Louisville, KY 40292, USA, , , , , , US.
Large River Studies Center, Biology Department, Winona State University, Winona, MN 55987, USA, , , , , , US.
Oecologia. 1998 Dec;117(4):551-563. doi: 10.1007/s004420050692.
Analyses of stable isotope (δC and δN) and C:N ratios of food webs within a floodplain and a constricted-channel region of the Ohio River during October 1993 and July 1994 indicate that the increasingly influential flood pulse concept (FPC) does not, for either location, adequately address food web structure for this very large river. Furthermore, results of this study suggest that the riverine productivity model (RPM) is more appropriate than the widely known river continuum concept (RCC) for the constricted region of this river. These␣conclusions are based on stable isotope analyses of potential sources of organic matter (riparian C trees, riparian C grasses and agricultural crops, submerged macrophytes, benthic filamentous algae, benthic particulate organic matter, and transported organic matter containing detritus and phytoplankton) and various functional feeding groups of invertebrate and fish consumers. The FPC, which stresses the key contribution of organic matter, particularly terrestrial organic matter, originating from the floodplain to riverine food webs, was judged inappropriate for the floodplain region of the Ohio River for hydrodynamic and biotic reasons. The rising limb and peak period of discharge typically occur in November through March when temperatures are low (generally much less than 10°C) and greater than bank-full conditions are relatively unpredictable and short-lived. The major food potentially available to riverine organisms migrating into the floodplain would be decaying vegetation because autotrophic production is temperature and light limited and terrestrial insect production is minimal at that time. It is clear from our data that terrestrial C plants contribute little, if anything, to the consumer food web (based on δC values), and δN values for C plants, coarse benthic organic matter, and fine benthic organic matter were too depleted (∼7-12‰ lower than most invertebrate consumer values) for this organic matter to be supporting the food web. The RPM, which emphasizes the primary role of autotrophic production in large rivers, is the most viable of the remaining two ecosystem models for the constricted-channel region of the Ohio based on stable isotope linkage between sources and consumers of organic matter in the food web. The most important form of food web organic matter is apparently transported (suspended) fine (FTOM) and ultra-fine particulate organic matter. We propose that phytoplankton and detritus of an autochthonous origin in the seston would represent a more usable energy source for benthic (bivalve molluscs, hydropsychid caddisflies) and planktonic (microcrustaceans) suspension feeders than the more refractory allochthonous materials derived from upstream processing of terrestrial organic matter. Benthic grazers depend heavily on nonfilamentous benthic algae (based on gut analysis from a separate study), but filamentous benthic algae have no apparent connection to invertebrate consumers (based on δC values). Amphipod and crayfish show a strong relationship to aquatic macrophytes (possibly through detrital organic matter rather than living plant tissue). These observations contrast with the prediction of the RCC that food webs in large rivers are based principally on refractory FTOM and dissolved organic matter from upstream inefficiencies in organic-matter processing and the bacteria growing upon these suspended or dissolved detrital compounds. The conclusions drawn here for the Ohio River cannot yet be extended to other floodplain and constricted-channel rivers in temperate and tropical latitudes until more comparable data are available on relatively pristine and moderately regulated rivers.
对俄亥俄河漫滩和狭窄河道区域内食物网的稳定同位素(δC和δN)及C:N比值在1993年10月和1994年7月期间的分析表明,对于这两个区域中的任何一个而言,影响力日益增大的洪水脉冲概念(FPC)都未能充分阐释这条大河的食物网结构。此外,本研究结果表明,对于该河的狭窄区域,河流生产力模型(RPM)比广为人知的河流连续体概念(RCC)更为适用。这些结论基于对潜在有机物质来源(河岸C类树木、河岸C类草本植物和农作物、沉水大型植物、底栖丝状藻类、底栖颗粒有机物以及含有碎屑和浮游植物的输送有机物质)以及无脊椎动物和鱼类消费者的各种功能摄食组的稳定同位素分析。由于水动力和生物因素,强调源自漫滩的有机物质(尤其是陆地有机物质)对河流食物网的关键贡献的FPC,被判定不适用于俄亥俄河的漫滩区域。流量的上升阶段和峰值期通常出现在11月至次年3月,此时气温较低(一般远低于10°C),超过满岸水位的情况相对难以预测且持续时间较短。迁移至漫滩的河流生物可获取的主要食物可能是腐烂的植被,因为自养生产受温度和光照限制,且此时陆地昆虫产量极低。从我们的数据可以明显看出,陆地C类植物对消费者食物网的贡献微乎其微(基于δC值),而且C类植物、粗底栖有机物和细底栖有机物的δN值过低(比大多数无脊椎动物消费者的值低约7 - 12‰),以至于这些有机物无法支撑食物网。基于食物网中有机物质来源与消费者之间的稳定同位素联系,强调自养生产在大河中主要作用的RPM,是俄亥俄河狭窄河道区域剩余的两个生态系统模型中最可行的。食物网有机物质最重要的形式显然是输送(悬浮)的细颗粒(FTOM)和超细颗粒有机物质。我们认为,相对于源自陆地有机物质上游处理的更难分解的外来物质,浮游生物中本地起源的浮游植物和碎屑对底栖(双壳贝类软体动物、纹石蛾科毛翅目昆虫)和浮游(小型甲壳类动物)悬浮摄食者而言是更可用的能量来源。底栖食草动物严重依赖非丝状底栖藻类(基于另一项单独研究的肠道分析),但丝状底栖藻类与无脊椎动物消费者并无明显联系(基于δC值)。端足类动物和小龙虾与水生大型植物有很强的关系(可能是通过碎屑有机物质而非活的植物组织)。这些观察结果与RCC的预测形成对比,RCC认为大河中的食物网主要基于难分解的FTOM以及上游有机物质处理效率低下产生的溶解有机物质,以及在这些悬浮或溶解的碎屑化合物上生长的细菌。在获得更多关于相对原始和适度调控河流的可比数据之前,此处针对俄亥俄河得出的结论尚不能推广至温带和热带地区的其他漫滩和狭窄河道河流。