基于遥感指数的草原火后植被恢复研究

草原火是草原生态系统重要的干扰因子，严重影响着系统的结构与功能。基于遥感数据，以2015年“4·16”特大草原火灾为例，利用ENVI和ArcGIS等软件，分别对NDVI和GPP指数及火烧严重度下的植被恢复过程进行定量分析。结果表明，基于NDVI和GPP指数的火后植被恢复过程表现相似，不同年份植被恢复情况存在一定差异。火灾发生当年（2015年）火烧迹地植被恢复状况高于未发生火灾区域，而在火后第1年（2016年）却又稍低于未发生火灾区域，直到火后第2年（2017年），火烧迹地植被基本恢复到火前状态。同时，不同火烧严重度下的植被恢复过程在存在明显差异。草原火灾发生后当年（2015年），中强度火烧下植被恢复最好，其次是轻度，重度表现最差。草原火烧严重度对植被恢复的影响，主要表现在火后第1个植被生长季。在之后的年份里，由于草原更新能力强大，不同火烧严重度对草原植被的影响不明显。本研究可丰富草原火灾及火烧迹地植被恢复等相关研究成果，同时为草原火灾管理和草原生态系统的可持续发展提供科学依据。     

河北省天然草地禾本科植物的生活型、生态型及区系分析

对河北省天然草地禾本科植物的生活型、生态型及区系特征进行了分析，结果表明，多年生草本为优势生活型，占78．4％；生态型以中生植物为主，占77．2％，旱生植物占16．0％，湿生植物仅占6．8％；植物区系成分多样，温带分布属最多达42属，占总属数的57．5％，其次为热带分布属，有24属，占32．9％。     

高原鼠兔对草地植被的危害及防治阈值研究

对高原鼠兔在不同时期的危害特征进行了研究，针对该鼠在补偿危害期和非补偿危害期的危害量提出了一种估算方法，得出其群体全年平均危害量β（干重）为4．94kg／只。同时根据春季灭鼠率（k）、秋季种群数量变化的预测值（λ）以及群体平均危害量（β）等参数估算可挽回损失值y。当可挽回损失值与成本参数（c）相等时，春季防治的经济阈值（x）为19．09只／hm^2或63．6个洞口／hm^2。     

塔里木盆地北缘植被生活型组成的分析

塔里木盆地北缘地区共记录野生植物123种,在其生活型组成中,地面芽植物居首位,达35.6%,次为一年生植物占22.7%,表现本区植被具有温带荒漠的特殊属性。塔里木盆地为我国最干旱的内陆盆地。这一区域的环境及生物群的特点曾引起有关学者的广泛兴趣。上世纪末至本世纪初,普热瓦尔斯基、别夫佐夫、罗布拉夫斯基等曾先后在新疆进行考察,斯文赫定和斯坦因曾对胡杨作过描述,谢彬曾论及胡杨的分布。1957至1958年间,中国科学院新疆综考队对塔里木盆地的环境和植被进行了大量的工作。此后     

水电站虹吸式进水口的控制

在对河北省几座已建虹吸式进水口水电站的虹吸控制方式进行分析对比的基础上,给出了一种采用液气射流泵将虹吸体抽成“低管”正虹吸,用“Y”形管中的水封保持真空,事故时利用“高管”自动补气破坏真空的控制系统,并分析了该系统的特点,给出了设计计算方法及计算公式。     

新建县沙生植被的保护与开发利用

以农业生产为支柱产业的新建县地处鄱阳湖流域，区域内沙生植被较脆弱。随着经济与人口的快速增长及农、林、旅游业的大发展，如何保护县域内沙生植被、更好的开发和利用这种资源十分重要。在分析新建县沙生植被现状及影响其生长的主要因素的基础上，就该地区内沙生植被的保护和开发利用提出建议。     

更新林相图的计算机辅助方法

常规编制与更新林相图的方法要求昂贵的光学机械纠正仪器、较高的操作技术和成本。文章提出一种利用计算机辅助纠正航空象片更新林相图的方法,可以降低成本,提高成图效率。为了实现这种方法,首先根据航空摄影理论分析,推导出适合编程的航空纠正数字化线性模型和算法。该模型要求在底图和航片上有四对控制点坐标,求算纠正参数。采用数字化仪测定这些坐标,求解参数,然后根据该线性模型对航片上编图要素的数字化坐标进行非共面变换,进而更新林相图。为完成这一过程需要四个程序模块和处理流程。使用这种方法更新林相图既能保证精度要求,又具有操作简单的优点。     

高等级公路植被护坡工程技术发展初探

依据恢复生态学原理,在探讨植被护坡技术现状的基础上,对高等级公路植被护坡工程技术中的生物治理和工程治理进行分析,提出了植被护坡工程设计原则、技术发展趋势和建议.     

Rural depopulation and recent landscape changes in a Mediterranean region: Consequences to the breeding avifauna

We studied the vegetational and avifaunistic changes following rural depopulation in an area covering 2,600 ha north of Montpellier (Southern France). The study area is covered by a mosaic of Mediterranean habitats that includes cultivation, grasslands, shrublands, and woodlands and is representative of the natural features present and of the human usage practiced so far in this part of the Mediterranean. We sampled the vegetation and the bird fauna in the same 193 census plots in 1978 and in 1992. At both the habitat and landscape scales the cover of woody plants increased significantly. Open habitats tend to disappear. As a consequence the abundance of open-habitat bird species decreased significantly whereas the abundance of forest birds increased significantly. These changes favor a pool of forest species widespread in western Europe and reduce habitat availability for open habitat and shrubland species. Many of the latter are Mediterranean species whose distribution in Western Europe could become reduced under current landscape dynamics. Our observation of more woodlands and their typical birds and of less open habitats and their associated avifauna is not consistent with the traditional worry shown by the public and the managers about the regression of forests and woodlands in the Northern Mediterranean as a consequence of fire.     

An investigation of uncertainty in field habitat mapping and the implications for detecting land cover change

Land cover data for landscape ecological studies are frequently obtained by field survey. In the United Kingdom, temporally separated field surveys have been used to identify the locations and magnitudes of recent changes in land cover. However, such map data contain errors which may seriously hinder the identification of land cover change and the extent and locations of rare landscape features. This paper investigates the extent of the differences between two sets of maps derived from field surveys within the Northumberland National Park in 1991 and 1992. The method used in each survey was the Phase 1 approach of the Nature Conservancy Council of Great Britain. Differences between maps were greatest for the land cover types with the smallest areas. Overall spatial correspondence between maps was found to be only 44.4%. A maximum of 14.4% of the total area surveyed was found to have undergone genuine land cover change. The remaining discrepancies, equivalent to 41.2% of the total survey area, were attributed primarily to differences of land cover interpretation between surveyors (classification error). Differences in boundary locations (positional error) were also noted, but were found to be a relatively minor source of error. The implications for the detection of land cover change and habitat mapping are discussed.