莫莫格湿地干-湿界面优势植物种群动态分析

莫莫格湿地从高河漫滩底端到顶端选取有代表性的植物群落片断作为固定观测样带,并设置6个观测样方,生长季5月、7月、9月3次观测结果表明,小叶章优势种群5月份密度最高达1154-1594株/平方米,7月种群数量下降,9月有所升高;踏头苔草优势种群5-7月份密度在3 414-7 193株/平方米,9月份种群数量大幅度下降;土壤相对含水量低地段小叶章种群相对优势度大,土壤相对含水量高地段踏头苔草种群相对优势度大,局部地段生长季内有相对优势度相互替代过程,莫莫格湿地干-湿界面上小叶章和踏头苔草两个种群可以共存。     

四川新津白鹤滩国家湿地公园核心区植物景观配置研究

四川新津白鹤滩国家湿地公园位于成都市新津县境内,是典型的河流漫滩和沙洲地貌。受亚热带湿润气候影响,湿地公园核心区拥有种类丰富的湿地动植物资源,但近几年人们在场地周边的开发活动,对基地原有植物生态环境造成破坏_^[1]。现在核心区仅存那些对水质要求低和抗逆性强的植物,同时也因为植物种类过于单一,随之而来的就是湿地季节性功能失调现象,如对水质净化的能力差,水体富营养化严重。为缓解和改善湿地核心区现存问题,一个具有生态修复功能的植物景观配置就显得尤为重要,本论文主要以生态恢复学、植被演替理论等为理论支撑,借鉴LID技术在湿地生态修复的应用,结合对基地本身植物资源调查的基础,通过对不同植物的配置选择,构建起了多样的新旧植物景观模式,用以探索科学合理的湿地公园植物景观配置模式,以期恢复新津湿地公园植被生态多样性,提升视觉景观效果。     

浅议湿地公园环境教育体系之建设架构

通过分析湿地公园环境教育的目标和特点,进而得出环境教育的建设构架可分为环境解说、博览展示、参与体验三个方面,同时,通过不断对比各种教育受众特点等方法,得出结论:在湿地公园中开展环境教育是基于完善的科普宣教场所、完整的环境解说系统和合理的组织形式三者完美结合而实现的。     

内蒙古乌拉盖草原湿地中下游植被退化演替趋势分析

针对内蒙古锡林郭勒盟东乌旗乌拉盖草原湿地植被退化问题,采用植被生态调查方法进行生态损伤评估和植被演替趋势分析.调查结果表明:在乌拉盖河截流5年内,乌拉盖湿地中下游植被退化迅速,原生植被的建群种和优势种基本消失,群落高度和盖度迅速降低,原生植被群落重要值显著降低,次生植被群落重要值增加;植物种的数量大量减少,植物多样性严重降低;一年生草本植物数量和比例明显高于多年生草本植物,部分荒漠化严重地区还出现超旱生植物小果白刺(Nitraria sibirica Pall.);乌拉盖草原湿地已经从草原湿地植被演替为碱蓬盐化草甸植被和盐漠化裸地.     

榄溪菊韵的景观特色分析

小榄菊花会是广东省中山市小榄镇一项重要的民俗活动。以菊花会200周年景点之一的榄溪菊韵为例,从园林景观的角度分析了菊花与湿地景观融合、菊花与园林造景等方面的关系,为菊花在园林中的应用提供了新的思路,阐述弘扬小榄菊花文化和保护湿地的重要性。     

简述湿地公园总体布局及其保护对策

从3个方面分别介绍了吉林扶余大金碑湿地公园的概况、总体规划布局及保护利用对策。     

Linking habitat suitability and seed dispersal models in order to analyse the effectiveness of hydrological fen restoration strategies

The effectiveness of measures targeted at the restoration of populations of endangered species in anthropogenically dominated regions is often limited by a combination of insufficient restoration of habitat quality and dispersal failure. Therefore, the joint prediction of suitable habitat and seed dispersal in dependency of management actions is required for effective nature management. Here we demonstrate an approach, which links a habitat suitability and a seed dispersal model. The linked model describes potential species distribution as a function of current species distribution, species-specific dispersal traits, the number of successful dispersal events, dispersal infrastructure and habitat configuration. The last two variables were related to water management actions. We demonstrate the applicability of the model in a strategy analysis of hydrological restoration measures for a large fen area in which still numerous endangered plant species grow.With the aid of the linked model, we were able to optimise the spatial planning of restoration measures, taking into account both the constraints of water management practices on abiotic restoration and the effects of habitat fragmentation on dispersal. Moreover, we could demonstrate that stand-alone habitat suitability models, which assume unlimited dispersal, may considerably overestimate restoration prospects. For these reasons, we conclude that linked habitat suitability and dispersal models can provide useful insights into spatially differentiated potentials and constraints of nature restoration measures targeted at the sustainable conservation of endangered plant populations whose habitats have been deteriorated due to undesirable effects of land and water management on abiotic conditions. These insights may contribute to the design of cost-effective nature restoration and conservation measures.     

湿地沉积物重金属环境化学行为研究进展

湿地沉积物重金属污染是当前环境科学领域的研究热点.本文在简要回顾国内外湿地沉积物中重金属污染研究成果的基础上,从湿地沉积物重金属来源、形态组成及提取方法、重金属在沉积物-水界面的迁移转化、质量基准以及风险评价等方面综述了当前国内外研究的最新进展,并提出了该领域未来可能的研究方向.认为针对湿地沉积物重金属向水体释放引起的二次污染问题,应重点对湿地沉积物重金属的环境化学行为展开深入研究,在研究方法和研究手段上应注重新技术的开发与应用.     

基于MODIS和NOAA数据尺度转换的若尔盖植被变化研究

为获得若尔盖地区较长时间序列的遥感植被指数,采用重采样技术和一元线性回归方法实现了GIMMS NDVI和MODIS NDVI的空间尺度转换和时间尺度外推。结果表明:（1）不同重采样方法对MODIS NDVI数据的影响与空间尺度有关,对GIMMS NDVI数据的影响则与空间尺度关系不大;（2）空间分辨率2.5 km,对不同植被类型可建立GIMMS NDVI和MODIS NDVI数据的一元线性转换关系,利用GIMMS NDVI拟合的结果与MODIS数据的差值统计符合正态分布;（3）1982—2013年,以1998年为节点若尔盖地区的植被先退化后逐渐恢复,尽管近几年植被指数平均水平高于研究初期,但局部地区的植被退化形势仍然比较严峻。     

Dynamic of organic matter in the heavy fraction after abandonment of cultivated wetlands

The abandonment of cultivated wetland soil increased the contents of light fraction organic matter (LFOM), heavy fraction organic matter (HFOM) and soil organic matter (SOM). The LFOM and HFOM content increased to 13.3 g kg⁻¹ and 62.4 g kg⁻¹ after 5 years whereas they were 8.4 and 47.9 g kg⁻¹ after 9 years of cropping, respectively. Fourteen years after abandonment, HFOM content increased to 104.3 g kg⁻¹. LFOM was positively correlated with HFOM (p < 0.001). A Langmuir equation was used to calculate the highest HFOM value. The value for the natural wetland soil was closed to this theoretical value (140.8 g kg⁻¹). After 14 years of abandonment, the HFOM maximum (HFOM_Max) value was lower than the equilibrium value suggesting that a further increase in HFOM can occur after abandonment. Assuming a linear accumulation (3.87 Mg C ha⁻¹yr⁻¹), it would take approximately 24 years after the abandonment to reach the HFOM_Max value.