新疆艾比湖流域平原区景观植被属性特征研究

在对新疆艾比湖流域平原区进行景观生态分类的基础上,利用“3S”技术叠置研究区草地资源类型图与景观类型图,对研究区景观植被属性特征进行分析。结果表明,研究区主要为荒漠、草原和草甸,共有33个植物群落类型,小蓬荒漠、梭梭荒漠、刚毛柽柳荒漠等各类荒漠面积合计约占研究区总面积的74．10％,芦苇草甸、含胡杨的芦苇草甸及矮嵩草草甸等各类草甸及草原面积也较大,占研究区总面积的18．34％。     

基于CA-Markov模型的艾比湖流域平原区景观格局动态模拟预测

利用“3S”技术及CA-Markov模型,按照是否实施跨流域调水工程2种预案情况,以2005年为起始时刻,对新疆艾比湖流域平原区2020年景观格局进行模拟预测。结果显示：在调水工程未实施的情况下,2020年研究区的生态环境将进一步恶化,其突出表现为艾比湖湖泊水面将持续萎缩、裸露湖底盐漠面积进一步扩大,水资源短缺及生态环境恶化的结果将严重制约研究区社会经济的发展;在调水工程实施的情况下,2020年研究区内艾比湖湖泊水面将稳定增加至800 km^2以上、裸露湖底盐漠面积相应有所减少,生态环境恶化趋势得到改善,区域水资源短缺问题将有所缓解,可有效地促进研究区内社会经济的发展。     

干旱区内陆湖泊流域景观格局变化及其对生态环境的影响

以我国干旱区典型内陆湖泊流域——新疆艾比湖流域为研究区,对其平原区1990--2005年的景观格局动态变化特征进行了研究。结果表明,1990--2005年,研究区农田、湿地及人居地景观的面积增加,其中以农田景观的面积增加量最大;而林地、草地、沙地、戈壁和盐碱地景观的面积呈减少趋势,其中草地、盐碱地和林地景观面积减少较多;各景观类型中以盐碱地、林地、草地和戈壁的转出率较高,而以农田、人居地的转入率较高;研究区景观组份构成没有大的变化,戈壁依然是研究区景观的基质。景观格局变化对区域生态环境的影响主要表现为：农田斑块数量和面积的增加,加大了区域水资源利用压力;林地、草地斑块面积减少,使得平原区绿洲遭受风沙的危害性增大;沙地、戈壁和盐碱地面积减少,使绿洲不同区域生态环境呈现不同变化特征;湿地斑块面积略有增加,对减少艾比湖流域沙尘危害较为有利。     

干旱区内陆艾比湖流域平原区景观生态安全评价研究

在构建基于景观尺度的生态安全评价模型基础上,分析了1990-2005年干旱区内陆艾比湖流域平原区的景观生态安全变化特征。结果表明:研究区景观生态安全状况可以分为3个层次,并以河流、湖泊及沼泽为主的湿地景观所在区域的生态安全程度相对较高。1990-2005年,研究区生态安全状况呈现"V"字型变化趋势,其中生态安全评价指数相对较低区域的面积所占比例呈现先增加后减少、总体上趋于增加的状态;而生态安全指数相对较高区域的面积所占比例呈现先减少后增加、总体上趋于减少的状态。     

艾比湖流域核心区景观生态功能区划及生态调控措施研究

在探讨了景观生态功能区划的概念、原则及区划方法的基础上,以新疆艾比湖流域核心区为对象,采用叠置法并利用“3S”技术对研究区进行了自下而上的景观生态功能区的划分,共划分出4个景观生态功能区和9个景观生态功能亚区。分析了各景观功能区的主导生态功能、保护目标,并有针对性地提出了景观生态调控的工程措施和管理措施,为恢复和重建艾比湖流域景观生态安全格局提供科学的参考依据。     

金坛区景观格局时空变化及驱动力分析

基于2010—2015年江苏省常州市金坛区高分辨率遥感影像,综合分析了生态系统空间分布格局及其演变特征,初步揭示了生态系统的驱动力及其对生态系统格局变化的影响。结果表明,金坛区生态系统类型主要由农田、湿地、城镇构成,3者合占总面积的87. 8%; 2010年以来,金坛加快实施城市\"东扩南移\"战略,原有农田不断被蚕食,生态系统的聚集度、边界密度有所上升,城镇更加连片分布,城镇面积已接近2020年18 604. 7 hm~2的建设红线。     

乌鲁木齐市土地利用景观格局变化研究

运用GIS、RS技术及景观生态学理论和方法,基于乌鲁木齐市2006年和2010年遥感影像解译数据,对乌鲁木齐市5年间土地利用景观格局变化特征进行分析,分别从斑块类型和景观水平2个方面对研究区土地利用景观类型进行动态分析。揭示其变化原因和内在规律,为研究区生态治理提供数据支撑,对景观的规划与管理、资源的有效利用和生物多样性保护具有重要意义。     

基于RS/GIS的大辽河口湿地景观格局时空变化研究

基于1988、1995、2001和2007年的四期TM数据,应用GIS/RS技术与景观格局分析软件FRAGSTATS,定量分析大辽河口地区湿地景观格局的动态变化。结果表明,自1988年以来,大辽河口地区的湿地面积逐年增加,湿地景观多样性指数和均匀度指数呈现先降后升的趋势,景观破碎化程度增强。湿地类型变化主要表现在大量的自然湿地转化为人工湿地或人工景观,具体表现在转化为建筑用地、水稻田、养殖区。1988~1995年期间,大辽河口地区的环境质量下降,该地区生物生活环境的多样性降低,造成了一些物种种群数量的减少甚至消失;但是自1995年以后,该地区的景观多样性和均匀性升高,抗干扰能力增强,环境质量有所提高。研究区湿地景观格局的动态变化主要是受自然条件和人为活动干扰共同作用的结果。     

黄土高原沟壑区土地景观空间格局遥感分析

应用遥感图像采集信息，在ＧＩＳ支持下，建立空间信息库，进行嵌块大小、分维数、形状指数、优势度、多样性、相对丰富度、破碎度等指标计算，研究了黄土高原沟壑区淳化县泥河沟流域土地景观空间格局特征。结果表明，本区域景观类型比较简单，景观多样性比较低。建议在本区域特别是在沟缘线上下两侧，打埝修梯，植树造林，建筑成沿沟沿缘线数十米宽的生态廊道和景观网络，增加景观类型，提高景观多样性，进一步控制水土流失，不断改     

汕头市练江流域景观格局与水质的关联分析

水环境对景观格局的变化极为敏感,水域(湿地)面积、分布格局、水质、水文特征等的变化,与土地变化和人类活动有着密切的关系,明确影响水质变化的关键景观因子,对于深入了解景观格局对水质的影响机制具有重要的研究价值.该研究选择广东省汕头市练江流域为研究对象,以2019年TM卫星影像、水质监测以及工业点源污染数据为基础,利用Sp...     

艾比湖水体中氯离子测定方法分析

用氯离子选择电极法测定艾比湖水体中氯离子的含量,对测定条件进行了探讨。结果表明,标准曲线在1.0×10-1~1.0×10-4mol/L内呈良好的线性关系,回收率为96.4%~103%,RSD为3.41%~4.34%,该方法简便、快速、准确,在实际工作中应用效果较为满意。     

2001-2005年新疆植被覆盖动态变化及原因分析

利用2001-2005年新疆归一化植被指数NDVI,得出该时间段新疆植被覆盖整体呈增加趋势,但局部有退化现象.对2001 - 2005年植被覆盖变化原因进行了分析,阐明降水是新疆植被覆盖变化的主要驱动因子之一.     

Landscape Change and Ecosystem Classification in a Municipal District of a Small City (Isernia,Central Italy)

Landscape changes taking place from 1954 to 1992 in the muncipal district of Isernia city (Central Italy) were described in relation to a system of ecosystem classification. Isernia municipal district was selected for study because recent historic changes in this area represent a typical example of landscape transformation similar to many small cities of Italy and other Mediterranean countries. To assess overall changes, three land cover maps (scale 1:25,000) were derived from panchromatic aerial photographs and field surveys. These were then digitalised in a Geographic Information System. A Land Facet (LF) map was derived by combining a phytoclimatic, a lithostatigrafic and a topographic map, and then digitalised as data layers in the same GIS. Results demonstrated two main landscape transformation trends: forest and semi-natural areas increased (8%), whereas agricultural areas decreased (12%). The urban area was relatively small during the entire analysed period, growing from 1% in 1954, to just 5% in 1992. Forest coverage was significant on reliefs, on hillside ecosystems such as limestone and on clay and marl hills LF. Arable land was particularly significant in flat ecosystems with deeper soils, such as on recent alluvial plain LF. These temporal changes were interpreted as being related to the replacement of traditional farming methods (grazing pastures) with more intensive methods (crop fields), especially on alluvial plains.     

塔里木河下游土地利用格局的景观生态学评价

利用 1 988— 2 0 0 0年新疆塔里木河下游TM影像解译的土地覆盖 (土地利用图 )和景观多样性指数、斑块重要值、破碎度、分维数等景观生态学指标 ,进行了塔里木河下游土地利用格局的空间分布和时间动态分析。     

Landscape as a predictor of wetland condition: an evaluation of the Landscape Development Index (LDI) with a large reference wetland dataset from Ohio

RecentAbstract. Recent approaches to wetland assessment have advocated a multilevel approach which incorporates assessments based on landscape (remote sensing) data, on-site but “rapid” methods, and intensive methods where quantitative data is collected. Brown and Vivas (2004) recently pro- posed an assessment method that uses remote sensing information (Landscape Development Index or LDI) and propose that it may also be usable as a quantified human disturbance gradient. The LDI was evaluated using a large reference wetland data set from Ohio using land use percentages within a 1 km radius circle of the wetlands. The LDI had interpretable and significant relationships with another human disturbance gradient (the Ohio Rapid Assessment Method for Wetlands or ORAM) and with most metrics and scores from the Vegetation Index of Biotic Integrity (VIBI) developed for use in the State of Ohio. Metrics from emergent wetlands had the most significant correlations with the LDI (10 of 10 metrics), followed by forested wetlands (8 of 10 metrics) and shrub wetlands (4 of 10). Poor correlation for VIBI scores and metrics of shrub wetlands was due to differences in attainable LDI scores based on ecoregion and natural buffers shielding the wetland from otherwise intensive land uses. The ORAM and VIBI were developed for use in wetlands in Ohio completely independent of the LDI. It is an important test of the LDI concept that so many interpretable and significant relationships occurred between the VIBI scores, VIBI metric values, and the ORAM scores. For the purposes of VIBI development, the LDI is an independent, quantified disturbance gradient that has provided an additional test of the VIBI. Given its theoretical underpinnings and the fact that it uses quantified land use percentages, the LDI has many advantages over more qualita- tive human disturbance gradients. Using land use percentages from increasingly smaller distances from the wetland edge (100-200 m) may improve the resolution of the LDI to detect on-site dis-turbances to a wetland which degrade its ecological condition. The LDI should be evaluated with other large reference data sets in other regions to evaluate its validity and usefulness as an assessment tool.