20年后大型无脊椎动物溪流流量研究:在溪流管理和恢复中的作用

J. Gore, J. Layzer, J. Mead
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引用次数: 170

摘要

在过去的二十年中,通过对河流流量评估的改进和应用,我们研究了水生大型无脊椎动物在各种条件下的水力栖息地,以及这些大型无脊椎动物在维持生态系统完整性方面的作用。溪流流量分析假定,河道流量特征的可预测变化可以反过来用于预测水生物种密度或分布的变化,或者更恰当地说,用于预测这些物种可用栖息地的可用性。五个主要的水力条件最能影响水生生物群的分布和生态成功:悬浮荷载、层载运动和水柱效应,如湍流、速度剖面和基质相互作用(近床水力学)。这些水力条件对单个生物体的形态和行为的相互作用决定了水生生物群的分布。从历史上看,利用物理栖息地模拟(PHABSIM)的管理决策主要集中在预测目标鱼类生命阶段的可用栖息地。监管机构很少将底栖生物的评估纳入流动储备。尽管“分类学上的不适”可能是不情愿使用或创建底栖动物标准的原因,但我们认为,对底栖大型无脊椎动物和鱼类群落之间联系的基本误解仍然是一个问题。这是由于缺乏可分配给大型无脊椎动物物种的感知价值。除了濒临灭绝的贻贝物种(PHABSIM分析可能不合适),这是可以理解的。然而,没有复杂的种群模型,预测大型无脊椎动物的分布(即对栖息地质量或位置变化的反应)和多样性的能力似乎更强。水质指标类群(蜉蝣目、翼翅目、毛翅目)生境适宜性标准;所谓的ept)也可能为流监管机构提供额外的管理选择。大型无脊椎动物标准的最大应用将是在低阶溪流中,在那里可以建立与鱼类群落更直接的联系。我们提出了一个来自美国北卡罗来纳州皇后溪的例子,在那里,保护底栖大型无脊椎动物群落完整性所需的每月分配明显高于目标底栖鱼类科图斯·贝迪。在大型无脊椎动物群落多样性处于瓶颈期的几个月里,只保护鱼类会导致大型无脊椎动物栖息地额外损失5-25%。我们建议,随着越来越多地强调维持大型无脊椎动物作为溪流健康监测者,将同时强调将水力栖息地条件纳入生物评估的一部分。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
Macroinvertebrate instream flow studies after 20 years: A role in stream management and restoration
Over the past two decades of refinement and application of instream flow evaluations, we have examined the hydraulic habitat of aquatic macroinvertebrates in a variety of conditions, along with the role of these macroinvertebrates in sustaining ecosystem integrity. Instream flow analyses assume that predictable changes in channel flow characteristics can, in turn, be used to predict the change in the density or distribution of lotic species or, more appropriately, the availability of useable habitat for those species. Five major hydraulic conditions most affect the distribution and ecological success of lotic biota: suspended load, bedload movement, and water column effects, such as turbulence, velocity profile, and substratum interactions (near-bed hydraulics). The interactions of these hydraulic conditions upon the morphology and behavior of the individual organisms govern the distribution of aquatic biota. Historically, management decisions employing the Physical Habitat Simulation (PHABSIM) have focused upon prediction of available habitat for life stages of target fish species. Regulatory agencies have rarely included evaluation of benthos for flow reservations. Although taxonomic discomfort' may be cited for the reluctant use or creation of benthic criteria, we suggest that a basic misunderstanding of the links between benthic macroinvertebrate and the fish communities is still a problem. This is derived from the lack of a perceived value' that can be assigned to macroinvertebrate species. With the exception of endangered mussel species (for which PHABSIM analysis is probably inappropriate), this is understandable. However, it appears that there is a greater ability to predict macroinvertebrate distribution (that is, a response to the change in habitat quality or location) and diversity without complex population models. Also, habitat suitability criteria for water quality indicator taxa (Ephemeroptera, Plecoptera, and Trichoptera; the so-called EPTs') may also provide additional management options to stream regulators. The greatest application for macroinvertebrate criteria will be in low-order streams where a more immediate link to fish communities can be established. We present an example from Queens Creek, in North Carolina, USA, in which monthly allocations required to preserve the integrity of the benthic macroinvertebrate community were significantly higher than for the target benthic fish species, Cottus bairdi. In the months when both Cottus and community diversity of macroinvertebrates were the bottleneck' life stages, preservation of only fish species could result in an additional 5-25% loss in macroinvertebrate habitat. We suggest that, as there becomes an increased emphasis on maintaining macroinvertebrates as monitors of stream health, there will be a concurrent emphasis on incorporating hydraulic habitat conditions as a part of bioassessment.
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