共查询到18条相似文献,搜索用时 93 毫秒
1.
2.
3.
21世纪初期,韩国首尔市政府完成了清溪川河道生态修复改造项目。该项目对于保护和恢复城市水空间、改善人民生活环境有巨大的贡献。文章以此为例结合韩国近现代社会的发展变迁,从河道治理、公众参与、近自然景观修复及文化历史融合等方面,分析和探讨了清溪川存在的问题和具体修复措施,对于现阶段城市水利建设的研究与实践提供借鉴与参考。 相似文献
4.
5.
6.
7.
结合辽宁省河流具体情况,将河流生态恢复尺度划分为空间尺度和时间尺度,空间尺度提出了“区域(水功能区、重要生态功能区、水土保持区)、流域、河流、河段”尺度及针对性河流生态恢复重点;时间尺度体现河流随时间推移发生的变化,将河流划分为极长、长、中、短时间尺度,确定了不同时间尺度河流恢复的研究内容。多种尺度相结合,可为河流生态恢复提供总体思路和治理方向。 相似文献
8.
奥地利维系河流健康生态的经验 总被引:2,自引:0,他引:2
维持河流健康生命日益成为国际社会的共识,1998~2000年奥地利启动的“健康河流行动”,体现了现代河流管理要强调把生态与防洪有机结合,努力实现恢复河流生态系统的六个原则:即自然发展、允许侵蚀、自然体系、自由流动、经济生态、大自然生长。这对我国正在探索的建设维系人水和谐的生态与环境具有积极的借鉴作用。 相似文献
9.
10.
城市河流作为城市环境要素的一部分,在城市发展中发挥着不可替代的作用,但由于过去粗放式的发展模式,引发了一系列生态环境问题,导致河流生态环境受损,河流部分功能丧失,影响了城市的未来发展。本文通过对当前城市河流普遍存在的问题进行分析总结,梳理了城市河流生态修复的发展历程。在此基础上,展望了未来的研究重点,可为我国的城市河流治理提供理论借鉴。 相似文献
11.
陈兴茹 《水利水电科技进展》2012,32(2):83-88
在分析国内外城市河流治理思路转变的基础上,介绍了以日本、韩国、美国和欧洲国家为代表的国外城市河流治理现状及我国目前在城市河流治理领域的研究现状及治理实例,指出了我国与国外发达国家在河流生态修复的思路、技术和方法上的差距,认为今后我国城市河流治理应更多地考虑城市河流与周围区域的整体关系、与带动经济和满足居民生活需求等多目标相结合等问题。 相似文献
12.
在简要介绍城市河流系统治理策略的基础上,详细论述其在鹅颈水生态修复中的应用。鹅颈水治理以流域为空间单位,准确把握河流主要问题,综合考量水资源、水安全、水环境、水生态、水文化,坚持工程和非工程措施并重,分阶段逐步实现洪水风险管理、外源污染控制、河流水质修复、河流生态系统恢复的目标。结果表明,鹅颈水目前已基本消除黑臭,水质逐渐提升至国家地表水Ⅳ类水标准。提出进一步加强河流生态系统恢复、优化管理制度、逐步建立全过程和全指标生态监测评估体系、实施弹性管理等鹅颈水系统治理措施。 相似文献
13.
14.
试论河流生态修复规划的原则 总被引:21,自引:1,他引:21
在指明河流生态修复的目的、任务的基础上,提出了河流生态修复规划的五条原则,即河流生态修复与社会经济协调发展的原则;流域尺度规划原则;增强空间异质性的景观格局原则;以生态自我修复为主.人工适度干预为辅的原则;生态修复工程与资源、环境管理相结合的原则。 相似文献
15.
介绍了河流治理要以生态水工学的理念进行生态整治,通过表述了遭到破坏的河流生态系统所面临的问题,即进行生态修复首先要治污、要满足河流的最低生态需水量、尽量恢复河流的自然状态,进一步从不同角度介绍生态修复的各种措施即从点、线、面、体各方位考虑生态修复。 相似文献
16.
针对伊利诺伊河流域的Emiquon区域以及肖托夸湖泥沙淤积问题。运用CHHMS耦合模型(Coupled Hydrology and Hydraulics Model System)对研究区域在不同泄洪开口组合的泥沙分布进行模拟,并根据不同流速状态下的颗粒流线图进行模拟得到沉淀物分布状况,结合湿地植物及鱼类生长需求对结果进行分析。研究发现CHHMS耦合模型在河流生态修复的模拟运用中具有很高的可开发性和实用性,经过模型模拟得到研究区域的合理规划方式,并且在成功利用河流到蓄滞洪区开口的情况下,水量以及泥沙沉淀物得到有效的控制,植被得到恢复,湿地的生态状况得到有效的改善。 相似文献
17.
18.
In December 2008, the draft programmes of measures (PoM) have been published in the EU member states, which list the measures that will be taken to enhance the ecological status of surface and groundwater bodies, and to reach the environmental objectives of the EU‐Water Framework Directive (WFD). We have analysed the German PoM to identify the main pressures and the restoration measures water managers planned to implement in streams and rivers. The objective was to evaluate the PoM and to identify the main, practically relevant knowledge gaps in river management on which applied river research should focus on. In general, the selection of measures in the PoM was reasonable. In accordance with the analysis of pressures and impacts in Germany, the PoM focussed on measures addressing morphological alterations and river continuity, and the results indicated that diffuse source pollution and fine sediment input were additional main pressures in Central European streams and rivers. Although point source pollution was not a main pressure in most rivers, respective point source measures have been selected for many water bodies. Apparently, these were so‐called basic measures that have to be taken due to other EU‐Directives or national laws. Therefore, although in line with the WFD, it seemed doubtful if the point source measures would help to substantially enhance the ecological status. Furthermore, the results indicated that there was a general lack of knowledge on the effect of restoration measures and a specific knowledge gap in how to enhance the ecological state of heavily modified water bodies (HMWB) in the lowland region with a high land‐use pressure, which was reflected by the high share of water bodies for which conceptual measures have been selected (e.g. developing management plans). Based on the analysis of the PoM and a literature review, we identified the following, practically relevant knowledge gaps in river management: (i) the morphodynamics of river reaches where natural channel dynamics have been restored, (ii) the combined effect of measures addressing diffuse nutrient and fine sediment input at different spatial scales (e.g. riparian buffer strips and land‐use changes), (iii) methods to identify suitable and efficient measures and to define environmental objectives for HMWB and (iv) the effect of measures on less well‐studied biological groups like macrophytes and phytoplankton. There is a strong need to summarize recent research results on these issues, to identify the knowledge gaps and research needs in detail, and to make the results of such a comprehensive literature review or meta‐analysis available for the next 6‐year management cycle and second WFD management plans. Copyright © 2010 John Wiley & Sons, Ltd. 相似文献