The role of Nature-Based Solutions for the water flow management in a Mediterranean urban area

IF 3.9 2区 环境科学与生态学 Q1 ECOLOGY Ecological Engineering Pub Date : 2024-08-31 DOI:10.1016/j.ecoleng.2024.107375
L. Sciuto , F. Licciardello , V. Scavera , D. Verde , E.R. Giuffrida , G.L. Cirelli
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Abstract

Due to climate change and rapid urban sprawl, central Mediterranean regions are subjected to short but intensive storm events resulting in a significant increase of flow rates and runoff volumes in low-lying coastal urban areas. Within the framework of green urban infrastructures (GUIs), a suitable combination of Nature-Based Solutions (NBS) with traditional grey infrastructures should be adopted to mitigate flood risk effects in urban and sub-urban areas contributing at the same time to achieve multiple benefits for both the environment and the community. The aim of this study is (i) to evaluate flood hazard maps for identifying the areas within a Sicilian hydrological river basin (Toscano catchment) with a high risk of flooding by implementing the HEC-RAS model at catchment scale; (ii) to quantify the peak flow and floodplain area reduction; (iii) to assess the effectiveness of small-scale NBS (green roofs, porous pavements, rain gardens and rain barrel), in terms of peak flow and runoff volume reductions, at urban block scale by using the EPA SWMM model Model simulations are performed integrating the hydraulic (HEC-RAS) and hydrological (EPA SWMM) models for return periods of 10, 50 and 200 years. The results showed that the estimated peak flow (m3 s−1) obtained from the simulations performed at catchment scale for each T in the current scenario (without NBS) using HEC-RAS and EPA SWMM models are very close to each other (R2 = 0.99). In addition, the utopian scenario simulation showed the HEC-RAS model sensitivity to CN calibration achieving a peak flow reduction up to about 60% with the floodplain area decreasing up to about 17%. Finally, the model EPA SWMM shows its sensitivity to NBS implementation at urban block scale with a peak flow reduction up to about 16% and a runoff volume (mm) reduction up to about 24%. These reductions decrease as T increases with a higher NBS mitigation effects for the lowest T. The results highlighted that the integration of NBS in urban areas could have hydrological and hydraulic positive effects, particularly in terms of peak flow and runoff volume reduction. Furthermore, the results suggest that small-scale NBS have a potential to be effective to smaller rainfall events, but a combination with large-scale NBS is necessary to cope with extreme events.

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基于自然的解决方案在地中海城市地区水流管理中的作用
由于气候变化和城市的快速扩张,地中海中部地区遭受着短时但密集的暴雨袭击,导致低洼沿海城市地区的流速和径流量显著增加。在绿色城市基础设施(GUI)的框架内,应将基于自然的解决方案(NBS)与传统的灰色基础设施适当结合,以减轻城市和城郊地区的洪水风险影响,同时为环境和社区带来多重效益。本研究的目的是:(i) 评估洪水灾害图,通过在流域范围内实施 HEC-RAS 模型,确定西西里水文流域(托斯卡诺流域)内洪水风险较高的区域;(ii) 量化洪峰流量和洪泛区面积的减少;(iii) 通过使用 EPA SWMM 模型,在城市街区范围内评估小规模 NBS(绿色屋顶、多孔路面、雨水花园和雨水筒)在减少峰值流量和径流量方面的效果 模型模拟综合了 10 年、50 年和 200 年回归期的水力模型(HEC-RAS)和水文模型(EPA SWMM)。结果表明,使用 HEC-RAS 和 EPA SWMM 模型对当前方案(无 NBS)中每个 T 的集水区规模进行模拟得出的估计峰值流量(m3 s-1)非常接近(R2 = 0.99)。此外,乌托邦情景模拟显示,HEC-RAS 模型对 CN 校准的敏感性可使峰值流量减少约 60%,洪泛区面积减少约 17%。最后,EPA SWMM 模型显示了其对在城市街区范围内实施 NBS 的敏感性,峰值流量减少了约 16%,径流量(毫米)减少了约 24%。这些减少量随着 T 的增加而减少,最低 T 的 NBS 缓解效果较高。结果突出表明,在城市地区整合 NBS 可产生积极的水文和水力效果,尤其是在峰值流量和径流量减少方面。此外,研究结果表明,小规模的泥沙淤积系统有可能对较小的降雨事件有效,但要应对极端事件,则需要与大规模的泥沙淤积系统相结合。
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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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