Organism-scale interaction with hydraulic conditions

IF 4.6 Q2 ENVIRONMENTAL SCIENCES Journal of ecohydraulics Pub Date : 2022-01-02 DOI:10.1080/24705357.2022.2042919
H. Nepf, S. Puijalon, H. Capra
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引用次数: 2

Abstract

Aquatic vegetation provides many ecosystem services with an estimated annual value of more than four trillion dollars (Costanza et al. 1997, Thomaz 2021). The services are strongly mediated by the interaction with hydraulics. Vegetation attenuates waves and current, protecting shorelines from erosion (e.g. Barbier et al. 2011; Arkema et al. 2017; Fonseca et al. 2019). Narayan et al. (2017) estimated that coastal marshes reduced flood damage due to Hurricane Sandy by $625 million. Further, the low energy environments created within vegetation provide nursery habitat for important fisheries (Costanza et al. 1997; Thomaz 2021) and promote the capture and retention of carbon carried in suspension, which contributes to the ability of aquatic vegetation to sequester larger amounts of carbon per hectare per year than rainforests (e.g. Fourqurean et al. 2012). Increasing hydrodynamic intensity can enhance nutrient uptake by individual plants (e.g. Lei and Nepf 2016; Gillis et al. 2017), but can also threaten vegetation survival (Katwijk et al. 2016). Because aquatic vegetation plays such an important role in protecting coastal environments and enhancing biodiversity, its protection and restoration have become a major focus in environmental management (Greiner et al. 2013; Sutton-Grier et al. 2015). On the other hand, excessive development of aquatic vegetation reduces channel discharge capacity, elevating flood risk. A better prediction of the hydrodynamic resistance generated by different species and areal distributions would enable managers to avoid this negative impact of vegetation. Management of vegetated landscapes, including restoration, depend on an understanding of the feedbacks between hydraulic conditions and vegetation growth and expansion (e.g. van Hulzen et al. 2007; Vandenbruwaene et al. 2011; Kondziolka and Nepf 2014). Similarly, the habitat selection and life-cycle behavior of aquatic invertebrates are closely linked to the organism-scale interaction with hydraulic conditions (e.g. Statzner et al. 1988; Smith et al. 2014; Lechner et al. 2016). Water depth, velocity, bed shear stress, and turbulence can influence habitat selection of macroinvertebrates and fish (e.g. Lamouroux et al. 1999; Dol edec et al. 2007); the swimming of fish larvae (Prada et al. 2018) and the migration of adult fish (Pavlov et al. 2008). Changes in land-use, installation of dams, and river regulation can all modify the hydraulic conditions, often having a negative impact on habitats and life-cycles. A better understanding of how hydraulics impact habitat and migration is needed to improve the restoration and management of freshwater fisheries and water resources.
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生物尺度与水力条件的相互作用
水生植被提供了许多生态系统服务,估计年价值超过4万亿美元(Costanza et al. 1997, Thomaz 2021)。这些服务是由与液压系统的相互作用强烈调节的。植被减弱波浪和水流,保护海岸线免受侵蚀(如Barbier等,2011;Arkema et al. 2017;Fonseca et al. 2019)。Narayan等人(2017)估计,沿海沼泽减少了飓风桑迪造成的洪水损失6.25亿美元。此外,在植被内创造的低能量环境为重要的渔业提供了苗圃栖息地(Costanza等,1997;Thomaz 2021),并促进悬浮碳的捕获和保留,这有助于水生植被比雨林每年每公顷吸收更多的碳(例如Fourqurean et al. 2012)。增加水动力强度可以增加单个植物对养分的吸收(例如Lei和Nepf 2016;Gillis et al. 2017),但也会威胁植被的生存(Katwijk et al. 2016)。由于水生植被在保护沿海环境和增强生物多样性方面具有重要作用,其保护和恢复已成为环境管理的重点(Greiner et al. 2013;Sutton-Grier et al. 2015)。另一方面,水生植被的过度开发降低了河道的流量,增加了洪水的风险。更好地预测不同物种和区域分布产生的水动力阻力将使管理人员能够避免植被的这种负面影响。植被景观的管理,包括恢复,取决于对水力条件与植被生长和扩张之间反馈的理解(例如van Hulzen等人,2007;Vandenbruwaene et al. 2011;Kondziolka and Nepf 2014)。同样,水生无脊椎动物的栖息地选择和生命周期行为与生物尺度与水力条件的相互作用密切相关(例如,Statzner et al. 1988;Smith et al. 2014;Lechner et al. 2016)。水深、流速、河床剪应力和湍流可以影响大型无脊椎动物和鱼类的栖息地选择(例如Lamouroux et al. 1999;Dol edec et al. 2007);鱼类幼虫的游动(Prada et al. 2018)和成鱼的洄游(Pavlov et al. 2008)。土地利用的变化、水坝的安装和河流管理都可以改变水力条件,通常对栖息地和生命周期产生负面影响。为了改善淡水渔业和水资源的恢复和管理,需要更好地了解水力学如何影响栖息地和迁徙。
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