通过有管理的调整与沉积物滋养,以自然为基础减轻潮汐沼泽地的海岸线侵蚀风险

IF 3.9 2区 环境科学与生态学 Q1 ECOLOGY
Marte M. Stoorvogel , Pim W.J.M. Willemsen , Jim van Belzen , Stijn Temmerman , Jan M. de Jonge , Johan van de Koppel , Tjeerd J. Bouma
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引用次数: 0

摘要

潮汐沼泽提供了许多宝贵的生态系统服务,通过减弱海浪和增加抗侵蚀能力,潮汐沼泽可以在低洼海岸和河口地区发挥重要的自然洪水风险缓解作用。世界各地都在努力恢复或创建潮汐沼泽,但人们仍然不知道不同的沼泽恢复和创建技术如何影响抗侵蚀沉积床的发展,而这对于潮汐沼泽为长期侵蚀和减轻洪水风险所做的贡献至关重要。在此,我们比较了在极高流速下(即沼泽后方的堤坝或海堤被冲垮时可能出现的情况),有管理的调整场地与沉积物滋养场地的沉积物剪切强度和抗侵蚀能力,分别进行了恢复和创建,并评估了潮汐淹没、沉积物特征和植被的影响。有管理的调整包括向陆地迁移海堤和堤坝等防洪设施,以及潮水淹没低洼地,为细粒沉积物的潮汐沉积创造有利环境,而沉积物滋养则是向海边放置大部分较粗粒的疏浚沉积物。这项研究表明,在这两个地点,有植被地点的沉积物剪切强度和抗侵蚀能力均高于无植被地点。此外,在有管理的调整地点,潮汐淹没持续时间对剪切强度有负面影响,而体积密度对剪切强度有正面影响。在泥沙淤积地点,除植被外,泥沙粒径是剪切强度和抗侵蚀能力的最重要驱动因素:随着泥沙粒径的增加,剪切强度和抗侵蚀能力都在下降。在快速形成抗侵蚀沉积床方面,人工调整和沉积物滋养各有利弊。人工调整可能会产生细粒度、粘性沉积物,在这种情况下,这些沉积物会被茂密但生长缓慢的嗜泥植物斯巴达植物所覆盖。与此相反,沉积物滋养通常使用的是颗粒较粗、无粘性的沉积物,在这种情况下,这些沉积物最初会被稀疏但生长迅速的沙棘植被所覆盖。茂密的斯巴达草比稀疏的沙棘草更能提高抗侵蚀能力。如果我们提前做好规划,并暂时支持它们的发展,恢复或创建的沼泽就有时间变得具有抗侵蚀能力,从而能够可持续地利用沼泽生态系统服务,长期缓解基于自然的洪水风险。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
Nature-based mitigation of shoreline erosion risks in tidal marshes created by managed realignment vs. sediment nourishment
Tidal marshes provide many valuable ecosystem services and can play an important role in nature-based flood risk mitigation along low-lying coasts and estuaries, by attenuating waves and increasing erosion resistance. There is an effort around the world to restore or create tidal marshes, but it remains unknown how different marsh restoration and creation techniques affect the development of erosion resistant sediment beds, which is essential for their contribution to long-term erosion and flood risk mitigation. Here, we compared sediment shear strength and erosion resistance under very high flow velocity (i.e. as may occur during the breach of a dike or seawall behind the marsh) of a managed realignment site versus a sediment nourishment site, restored and created respectively, and assessed the effects of tidal inundation, sediment characteristics, and vegetation. Managed realignment consists of the landward relocation of flood defence structures like seawalls and dikes and tidal flooding of low-lying land, creating a sheltered environment for tidal deposition of fine-grained sediments, while sediment nourishment is the seaward placement of mostly more coarse-grained dredged sediment. This study showed that at both sites sediment shear strength and erosion resistance were higher at vegetated locations than at unvegetated locations. In addition, at the managed realignment site, tidal inundation duration affected shear strength negatively, while bulk density affected shear strength positively. At the sediment nourishment site, sediment grain size was the most important driving factor of shear strength and erosion resistance, besides vegetation presence: a decreasing shear strength and erosion resistance were observed with increasing sediment grain size. Managed realignment and sediment nourishment both have advantages and disadvantages for the fast development of an erosion resistant sediment bed. Managed realignment will likely lead to fine-grained, cohesive sediments, which are in this case colonised by dense, but slowly establishing, mud-loving Spartina vegetation. In contrast, sediment nourishments are typically done with more coarse-grained, non-cohesive sediments, which are in this case colonised by initially sparse, fast establishing Salicornia vegetation. Dense Spartina increased erosion resistance more than sparse Salicornia. If we plan well ahead of time and temporarily support their development, restored or created marshes have time to become erosion resistant, thereby enabling sustainable use of marsh ecosystem services for long-term nature-based flood risk mitigation.
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来源期刊
Ecological Engineering
Ecological Engineering 环境科学-工程:环境
CiteScore
8.00
自引率
5.30%
发文量
293
审稿时长
57 days
期刊介绍: Ecological engineering has been defined as the design of ecosystems for the mutual benefit of humans and nature. The journal is meant for ecologists who, because of their research interests or occupation, are involved in designing, monitoring, or restoring ecosystems, and can serve as a bridge between ecologists and engineers. Specific topics covered in the journal include: habitat reconstruction; ecotechnology; synthetic ecology; bioengineering; restoration ecology; ecology conservation; ecosystem rehabilitation; stream and river restoration; reclamation ecology; non-renewable resource conservation. Descriptions of specific applications of ecological engineering are acceptable only when situated within context of adding novelty to current research and emphasizing ecosystem restoration. We do not accept purely descriptive reports on ecosystem structures (such as vegetation surveys), purely physical assessment of materials that can be used for ecological restoration, small-model studies carried out in the laboratory or greenhouse with artificial (waste)water or crop studies, or case studies on conventional wastewater treatment and eutrophication that do not offer an ecosystem restoration approach within the paper.
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