基于人工社会模型的退田还湖生态补偿机制实例研究

基于补偿者和受偿者意愿的研究方法是建立切实可行的生态补偿机制的有效手段。为探讨在我国许多地区开展退田还湖生态补偿政策的有效实施机制,减少洪涝灾害与生态环境退化负面效应,研究构建了基于农户、政府和企业三类主体及其相互作用的生态补偿模型,并重点分析生态补偿标准、洪灾风险、生态环境保护、劳动力本地转移政策等因素对农户主体土地利用决策的影响。以鄱阳湖区莲湖乡为实例,以农户和企业从事生产活动的行为特征和政府宏观调控方式为基本准则,利用构建的多主体模型模拟了不同补偿机制下退田还湖政策可能产生的土地利用长期效应。结果表明,政府给予农户的经济补偿可以使农户自愿实施退田,但在不同情景下,政府实施退田还湖的代价和达到预期目标的时限差距显著。企业参与不仅能减轻政府的经济负担,同时也有利于剩余农村劳动力的转移。政府发展壮大当地经济,提高农业劳动力向非农产业转移的速度和质量,均有助于推进退田还湖政策的有效实施。     

矿冶区重金属污染土壤肥力特征及生态修复潜力分析

通过对湖南长沙、株洲、衡阳和郴州地区典型矿冶区周边64个土壤样品的调查分析,结果表明,与我国《土壤环境质量标准》(GB15618-1995)III级标准(pH6.5～7.5)比较,典型矿冶区周边土壤中As、Cd、Pb和Zn含量的超标率分别为75.8%、75.8%、66.1%和71.0%,表现为多重金属污染。废弃地土壤中As、Cd、Cr、Cu、Pb和Zn含量显著高于菜地和水稻土壤中相应元素含量。典型矿冶区周边土壤整体呈酸性,质地较粘。土壤中有机质、碱解N、速效P、有效K含量范围分别为0.18～143g/kg、14.7～372、7.82～202、0.00～782mg/kg,其平均含量达到II级标准值的样品数分别占总样品数的93.7%、95.4%、100%和89.1%。土壤质地和肥力特征表明,典型矿冶区周边重金属污染土壤基本肥力总体水平较好,可以顺利开展其生态修复。     

Phosphorus release： A biogeochemical insight from a restored lakeside wetland in the Yangtze-Huaihe region, China

The heavy intensification of agriculture in East China since the 1980s caused the decrease of lake area and water storage capacity with impediment of regulation, lake eutrophication and frequent floods. Many restoration projects have been conducted. However, the knowledge of biogeochemical factors that drive nutrient cycles during the early stage of restoration is still limited. We studied the effect of the remediation of a patch of near-shore shallow wetland on the northern bank of Chaohu Lake in the Yangtze-Huaihe region, China, which was used as rice paddy for many years, on the behavior of phosphorus. Redox potential (ORP), temperature and dissolved oxygen were monitored in situ from May 2006 to November 2007. Samples of soil pore water were collected during this time for the determination of different forms of iron and phosphorus. ORP showed a clear transition of the wetland soil from an oxidized state in winter to a reduced state in summer. The decrease of ORP correlated with the release of large amounts of Fe and P. The maxima of total dissolved Fe and total dissolved P in the summer of the second year were (13.8 ± 6.8) mg/L and (0.88 ± 0.27) mg/L, respectively. It is worth noticing that P concentration far exceeded the critical value of lake eutrophication (0.02 mg/L). The pressure of P release to the adjacent lake during the first two years of wetland restoration from rice fields should be taken into account by environmental policy makers.     

Plant colonization of ex-arable fields from adjacent species-rich grasslands: The importance of dispersal vs. recruitment ability

Species-rich semi-natural grasslands have declined drastically in Europe over the last century and occur in modern landscapes as small and isolated fragments. Recreation of these species-rich plant communities and increasing connectivity of remaining grasslands are important goals for nature conservation. Ex-arable fields located adjacent to species-rich grasslands have been suggested as targets for such recreation, but we still lack knowledge about the processes determining colonization from grasslands to ex-arable fields. We examined transects from species-rich semi-natural grasslands to ex-arable fields in a nature reserve located in southeast Sweden, and analysed relationships between observed colonization of ex-arable fields and two characteristics of species: dispersal ability and recruitment ability. Colonization of ex-arable fields was not related to dispersal ability, assessed as adhesive potential to animal coat, wind dispersal potential and seed mass (related to seed production), but was positively related to recruitment ability, assessed by sowing experiment. The same relationships appeared when using a performance index from sowing experiments conducted in the UK. We conclude that recruitment ability is a key factor for colonization of ex-arable fields. In our study, around 50% of semi-natural grassland species were able to colonize adjacent ex-arable field margins spontaneously within a time window of less than 50 years. Seed sowing is however needed to increase the speed of the colonization process, because increasing seed density promotes colonization of species with poor recruitment in ex-arable fields. Actions to increase area and connectivity of species-rich grasslands should consider incorporating ex-arable fields.     

上海南汇东滩鸟类栖息地营造工程的生境评价

为应对长江口日益严峻的滨海湿地和鸟类栖息地丧失问题,上海南汇东滩鸟类栖息地营造工程采取地形构建与水位调控技术,营造了适宜鸟类栖息觅食的生态修复示范区。本项研究自2009年8月至2010年6月,跟踪监测了生态修复示范区内的植被生长参数(株高、密度、叶面积指数、地上生物量)、水体质量参数(氮磷营养盐和叶绿素a含量)以及土壤环境参数(电导率、pH值和重金属含量),分析和评价了该工程实施后的生态修复效果。结果表明,生态修复措施有效促进了本地物种芦苇群落的生长,一定程度上明显改善了示范区内的水体质量,维持了土壤重金属的低污染状态,有利于鸟类生物多样性的提高。说明南汇东滩鸟类栖息地营造工程取得了初步成效,呈现出较好的湿地修复效果。同时,应采取刈割与水位调节技术抑制外来物种互花米草,控制生态养殖规模,进一步改善鸟类栖息地生境质量。     

生态修复目标导向的河流生态功能分区初探

经济社会的快速发展不可避免的对河流生态系统造成了损伤,如何使受损河流生态系统恢复到健康状态已经成为当前亟待解决的重要环境问题之一.河流修复生态功能分区是对河流进行适应性生态修复的必要前提和基础,可为制定生态修复目标提供科学依据.本研究在已有分区体系基础上,依据生态功能分区的理论,对河流修复生态功能分区的内涵进行了辨析,...     

北美国家的湿地恢复及对中国太湖恢复的启示

以美国旧金山海湾带和加拿大安大略省沼泽湿地生态恢复为例,探讨了其成功经验,并指出了我国太湖恢复建设主要存在五个方面问题：理论技术体系相对滞后;恢复工程实施系统性缺乏;投融资方式单一化;恢复管理体系不完善;公众参与力度薄弱。据此提出相关建议,力求探索完善我国太湖生态恢复的有效路径。     

草地退化的因素和退化草地的恢复及其改良

草地退化是一个世界性的普遍问题。几乎所有的天然草原和人工草地,在利用不当时都可能出现这种现象。对草地退化的过程和原因比较复杂。草地生态系统的变化过程总是伴随着相关的地理、气候、土壤、灾害等各种自然因素的作用,有时一二种自然因素（如火或洪水）就可能造成生态系统的退化。所以对退化草地的恢复势在必行,本文着重对近几年较流行的退化草地的恢复方法进行了介绍。     

再生水回用于景观水体的富营养化问题和生态修复

由于营养物本底值较高,自净能力差,以再生水为水源的景观水体很容易产生水体富营养化,最终导致水华。文章介绍了国内外再生水回用于景观水体的进展,详细分析了景观水体富营养化的原因。针对水华问题,就近几年生态修复在富营养化景观水体方面的研究进展进行了总结,例如植物修复,动物修复和微生物修复对富营养化水体的修复。     

系统推进自然生态保护和治理能力建设——《全国重要生态系统保护和修复重大工程总体规划（2021—2035年）》专家笔谈

《全国重要生态系统保护和修复重大工程总体规划（2021—2035年）》是党的十九大后生态保护和修复领域第一个综合性规划,是多部门跨学科全区域统筹推进山水林田湖草一体化保护和修复的范式。针对规划贯彻实施面临的机遇和挑战,来自自然资源部咨询研究中心的7位专家进行了研讨。贯彻落实好《规划》,应准确把握规划的4个主要特点：布局上突出系统性和继承性;政策上突出战略性和协调性;实施上突出目标性和问题导向性;手段方法上突出科学性和针对性。处理好三大关系,即：生态系统保护与开发利用的关系,生态系统修复与生态补偿的关系,生态系统保护与用途管制的关系。解决八个关键问题：一是建设多元投融资机制;二是明晰主体责任;三是建立统一的综合性调查评价制度;四是构建适应生态系统修复的技术标准体系;五是建设生态系统保护数据库和综合信息查询平台;六是探索因地制宜的生态补偿模式;七是统筹自然资源开发利用与生态保护修复的关系;八是开展《规划》实施的跟踪监测评估。