武汉市湿地破碎化对生态系统服务价值的影响研究

以湖泊资源丰富的武汉市为例,通过景观格局指数测定该市湿地破碎化程度,借助GIS技术评估该市湿地生态系统服务价值,并探讨了城市湿地破碎化对生态系统服务价值的影响。结果表明:①2000—2015年武汉市湿地总体破碎化趋势有所缓和,但人工湿地相较于自然湿地破碎化程度要高,特别是2010—2015年湿地总面积下降了2.80%,而斑块密度上升了4.12%,湖泊破碎化程度较高。②2000—2015年,武汉市湿地ESV增长了323.27亿元,各类型湿地的生态系统服务价值表现为湖泊>水库坑塘>河流>沼泽。③湿地景观破碎化与部分调节性、支持性和文化性服务功能存在着显著相关关系。     

南四湖自然保护区生态环境遥感监测与评价

基于2000—2019年卫星遥感影像,分析山东省南四湖省级自然保护区2000年以来的土地利用状况,并计算其生态保护状况指数。结果表明:2000—2019年,南四湖省级自然保护区城乡建设用地面积呈增加趋势,水域湿地面积呈减少趋势。其中,湖泊等自然湿地面积减少,而水库坑塘、河渠等人工湿地增加。2000年以来,南四湖省级自然保护区生态保护状况总体为优。与2000年相比,生境质量指数略有下降,开发干扰指数逐年增大,自然保护区生态保护状况指数整体呈下降趋势。     

基于RS与GIS的莱州湾南岸滨海湿地景观类型与破碎化分析

应用Landsat--7遥感数据和GIS技术对莱州湾南岸滨海湿地类型、面积和分布现状进行了调查,并对滨海湿地景观特征及景观破碎化程度进行了分析.结果表明,研究区景观类型以盐田、滩涂和养殖池为主,人工湿地面积占整个湿地面积的78.22%.该区主要受人为干扰活动影响,区域景观斑块破碎化程度较高,对研究区湿地产生了严重的影响,因此合理调控人类干扰活动是改善莱州湾南岸滨海湿地环境的根本途径.     

伊犁河谷景观格局变化分析

景观生态学是宏观生态研究的一个新的领域.景观动态变化研究,是目前景观生态学中的一个研究热点.基于伊犁河谷2000年、2005年夏季有效时相Landsat TM/ETM 遥感影像资料,综合运用遥感与GIS技术,通过采用分维数,多样性指数,破碎度指数和边界密度等指数,分析了伊犁河谷景观动态变化.研究结果表明:①草地、水域和林地面积大幅度减少,耕地和城乡居民工矿交通用地猛增,城市化进程加快;②伊犁河谷斑块数目增多,景观边缘密度增加,景观破碎度增大,伊犁河谷景观异质性和景观形状的复杂性程度略微提升;③景观基质依然为草地,草地破碎度稍增,草地的多样性和异质性下降;④耕地的斑块数减少而斑块面积增大,破碎化程度降低,耕地的稳定性加强.     

岷江流域三江交汇区景观格局变化研究

本文以生态景观理论为基础,地理信息与遥感技术为支撑,对岷江流域三江交汇区三期遥感数据,1990年TM、2002年TM、2014年ETM+数据进行图像分类、景观指数提取、空间分析,同时采用面积转移矩阵统计各景观面积的转移情况,分析景观格局变化的影响因素,研究结果表明:(1)1990—2014年三江交汇区景观类型面积排序为:农田林地草地水域居民地裸地。优势景观为耕地,所占比例由72.83%下降到63.32%,面积减少了3480hm2。草地所占比例呈现波动变化,总体增加了2.81%。林地比例由15.98%上升到18.79%,增加了700hm2。居民地所占比例升高了4.1%;(2)1990年研究区内草地景观易受到外部干扰,其分布形状复杂。林地景观整体聚合度较高同时具有较低的异质性,分布通透性好、规模连续。农田分布较为分散且斑块较小。2002年农田斑块分布复杂化,同时具有聚集度高的特点。2014年研究区内农田优势地位下降。此时农田分布比较破碎并且呈现集中的态势。草地分布规模性较好、分布较为完整,但是内部存在一定的破碎性;(3)三江交汇区景观类型相互转化的主要原因:一是,退耕还林、还草政策实施,海拔超过500m的丘陵山地区域,建立生态保护区。二是,成绵乐铁路和高速路网的完善,使得三江交汇区的土地类型向建设用地转化加快,主要集中在乐山市中区和周围城镇。     

四川丘陵地区土地整理项目景观格局变化分析——以仪陇马鞍镇南海村土地整理项目为例

以仪陇马鞍镇南海村土地整理项目区为例,以土地整理前后1:2000实地调绘结果数据为基本数据源,采用景观格局指数分析其景观格局变化,探讨土地整理对景观变化的影响.结果表明,坡(地)改梯(田)后耕地中田块斑块数量和斑块密度增加,平均斑块面积和最大斑块指数减小,景观破碎度增加;耕地类中的旱地、农村宅基地及林地斑块数量和斑块密度降低,平均斑块面积和最大斑块指数增大,景观破碎度降低,景观形状较整理前变得规则;景观多样性指数和景观丰度指数降低,景观类型有所减少.     

不同生态区域油气田开发对土地覆盖变化的影响

利用RS-GIS技术,分析了四川合兴场气田周围1988年和2000年TM影像和新疆艾桑油气田周围1992年和2000年TM影像土地变化情况。分析结果表明:生态发达的四川合兴场气田周围在油田田开发前后主要为耕地,而建设用地在1988年占区域面积的12.6%,到2000年增加到17.8%。位于生态脆弱区的艾桑油气田,兴建前后主要土地利用类型均为戈壁荒漠、盐碱地,建设用地面积则明显增加,从1992年占总面积的0.02%增加到2000年的0.24%。由此可见,大面积分布式的油气田开发改变了油气田周围土地利用类型的分布。景观格局分析指数表明,四川合兴场周围多样性指数及均匀度指数均呈增加趋势,而艾桑油气田周围多样性指数及均匀度指数均呈现下降趋势。四川合兴场气田周围空间景观呈多样化发展,而新疆艾桑油气田周围空间景观多样性下降,荒漠土地呈扩大化发展趋势。     

基于RS和GIS的赛里木湖流域景观格局动态研究

基于RS和GIS的技术方法,运用景观格局指数对赛里木湖流域近25a来的景观格局变化综合分析。结果表明:1986-2010年,赛里木湖流域疏林地、灌木林地和中覆盖度草地面积增加,有林地、高覆盖度草地面积减小。整体上,景观斑块总数增加,景观破碎化指数、景观类型形状指数和景观多样性指数升高,均匀度指数有所减少。由此可以看出,该区域内由于自然或人为因素干扰所导致的景观斑块类型逐渐变得复杂,景观遭到破坏,土地利用向着多样化和非均匀化的方向发展,景观斑块分布变得很不均匀。     

惠来县景观格局与动态变化分析

在GIS技术和卫星遥感资料的支持下，利用景观格局分析软件FRAGSFATS3．3分析了揭阳市惠来县1994-2001年的土地景观格局的动态变化，并分别在类型水平上和景观水平上选择了部分景观指数。计算结果表明，破碎度趋向加深，景观结构和斑块形状复杂性增加（尤以林地和其它用地严重）；景观稳定性增加，优势度减少；景观多样性有所提高，受人类干扰程度加深，说明惠来县城市化速度快，处于城市发展的初期；各景观要素又有不同的景观动态特征。     

淮北市土地利用景观格局变化分析

以1987年和2000年TM影像为数据源,在ENVI 4.4平台下提取淮北市(相山建成区)1987-2000年土地利用/覆盖动态变化信息,利用FRAGSTATS 3.3软件提取研究区的斑块指数、多样性指数、优势度、破碎度、分维度及形状指数等景观格局指标,并进行分析.     

Effects of Land Use Changes on the Ecosystem Service Values of Coastal Wetlands

Changes in the coastal landscape of Southern Sinaloa (Mexico), between 2000 and 2010, were analyzed to relate spatial variations in wetlands extent with the provision and economic value of the ecosystem services (ES). Remote sensing techniques applied to Landsat TM imagery were used to evaluate land use/land cover changes while the value transfer method was used to assess the value of ES by land cover category. Five wetland types and other four land covers were found as representative of the coastal landscape. Findings reveal a 14 % decrease in the saltmarsh/forested mangrove area and a 12 % increase in the area of shrimp pond aquaculture (artificial wetland) during the study period. ES valuation shows that the total value flow increased by 9 % from $215 to $233 million (2007 USD) during the 10-year period. This increase is explained as result of the high value worldwide assigned to saltmarsh. We recognize limitations in the transfer-based approach in quantifying and mapping ES values in the region, but this method provides with value estimates spatially defined, and also provides some guidance in the preliminary screening of policies and projected development in the context of data-scarce regions.     

An inventory of wetland impoundments in the coastal zone of Louisiana,USA: Historical trends

We inventoried wetland impoundments in the Louisiana, USA, coastal zone from the late 1900s to 1985. Historically, impoundment of wetlands for reclamation resulted in direct wetland loss after levees (dikes) failed and the impounded area was permanently flooded, reverting not to wetland, but to open-water habitat. A current management approach is to surround wetlands by levees and water control structures, a practice termed semi-impoundment marsh management. The purpose of this semi-impoundment is to retard saltwater intrusion and reduce water level fluctuations in an attempt to reduce wetland loss, which is a serious problem in coastal Louisiana. In order to quantify the total impounded area, we used historic data and high-altitude infrared photography to map coastal impoundments. Our goal was to produce a documented inventory of wetlands intentionally impounded by levees in the coastal zone of Louisiana in order to provide a benchmark for further research. We inventoried 370,658 ha within the coastal zone that had been intentionally impounded before 1985. This area is equal to about 30% of the total wetland area in the coastal zone. Of that total area, approximately 12% (43,000 ha) is no longer impounded (i.e., failed impoundments; levees no longer exist or only remnants remain). Of the 328,000 ha still impounded, about 65% (214,000 ha) is developed (agriculture, aquaculture, urban and industrial development, and contained spoil). The remaining 35% (114,000 ha) of impoundments are in an undeveloped state (wetland or openwater habitat). In December 1985, approximately 50% (78,000 ha) of the undeveloped and failed impoundments were open-water habitat. This inventory will allow researchers to monitor future change in land-water ratios that occur within impounded wetlands and thus to assess the utility of coastal wetland management using impoundments.     

Changes in wetlands on nonfederal rural land of the conterminous United States from 1982 to 1987

Recent wetland area trends were estimated from the National Resources Inventory (NRI) for nonfederal rural lands for the period 1982–1987. NRI-based estimates of wetland area for states comprising the conterminous United States were highly correlated with estimates made by the US Fish and Wildlife Service and with estimates of coastal salt marsh wetlands made by the National Oceanic and Atmospheric Administration. Net wetland area declined by 1.1% (≈363,200 ha) during the five-year study period. Conversion to open water, primarily caused by natural flooding in western inland basins, was responsible for altering extensive wetland areas (≈171,400 ha). Of the human-induced wetland conversions, urban and built-up land was responsible for 48% of the wetland loss, while agricultural development was indicated in 37% of the converted wetland area. A decrease in rural land, and increases in both population, and urban and built-up land were associated with wetland loss among states. Potential reasons for wetland loss were different in 20 coastal states than in 28 inland states. Proportionately, wetland loss due to development was three times greater in coastal states than inland states, while agriculturally induced wetland losses were similar in both groups. The proportionate declines of forested vs nonforested wetlands were not significantly different among states.     

Wetland development trends in coastal North Carolina,USA, from 1970 to 1984

Coastal wetlands are a valuable resource to North Carolina, USA, representing important habitat for marine organisms and providing flood control areas and buffer zones from marine storms. An analysis of wetland development trends in coastal North Carolina from 1970 to 1984 was conducted using over 3000 files containing 15 years of permitting records. The total amount of coastal wetland area altered due to authorized development under the Coastal Area Management Act (CAMA), the Dredge and Fill Law, and Section 404 of the Federal Water Pollution Control Act is 1740 ha. This represents nearly 2% of the salt marsh wetlands along the coast of North Carolina. The number of permits issued steadily increased during the 1980s; however, the total amount of wetland loss decreased each year. A few large projects in the early 1970s accounted for nearly 70% of all wetland area developed during the 15-year period. Nearly two-thirds of all projects involving wetland destruction involved impacts on high marsh ecosystems. Bulkheads, canals, and filling activities made up 80% of the projects requiring permits; 62% of the permits were issued to private landowners, but this group accounted for only 16% of the losses of wetland area. Utility companies, which accounted for less than 1% of the permits issued, were responsible for 46% of the permitted wetland loss during the 15-year study period. Future studies should address agriculture and forestry practices which are exempt under CAMA laws and therefore their effects on wetland alteration have not been quantified.     

The Role of Wetlands for Mitigating Economic Damage from Hurricanes

Coastal communities along the United States coast often experience significant economic damage resulting from the impacts of tropical storms and hurricanes. Research suggests that certain factors that affect economic damages are increasing the vulnerability of coastal communities. Population growth, which increases vulnerability by placing valuable lives and assets in the path of storms, is expected to increase. Climate change has the potential to cause more frequent and intense storms, and coastal wetland loss is contributing to the vulnerability of coastal populations. Wetlands conservation and restoration is often advocated for as a means of reducing the impacts of coastal storms. The relationship between wetlands and storm surge energy is understood relatively well in physical terms, but very little economic analysis has been conducted to estimate the degree to which wetlands reduce economic impacts. Using factor analysis, the relationships among coastal populations, wetlands, storm intensity, and economic damage are explored. The factor analysis suggests that wetland presence is associated with a reduction in economic damages from coastal storms. Factor score analysis suggests that the proportion of damage explained by wetland presence is smaller for more intense storms. These results are consistent with those found in the physical science literature and have potentially large consequences for how wetlands are used in risk reduction.     

Rapid Mapping and Prioritisation of Wetland Sites in the Manawatu–Wanganui Region,New Zealand

The extent of wetland in New Zealand has decreased by approximately 90% since European settlement began in 1840. Remaining wetlands continue to be threatened by drainage, weeds, and pest invasion. This article presents a rapid method for broad-scale mapping and prioritising palustrine and estuarine wetlands for conservation. Classes of wetland (lacustrine, estuarine, riverine, marine, and palustrine) were mapped using Landsat ETM+ imagery and centre-points of palustrine and estuarine sites as ancillary data. The results shown are for the Manawatu–Wanganui region, which was found to have 3060 ha of palustrine and 250 ha of estuarine wetlands. To set conservation priorities, landscape indicators were computed from a land-cover map and a digital terrain model. Four global indicators were used (representativeness, area, surrounding naturalness, and connectivity), and each was assigned a value to score wetland sites in the region. The final score is an additive function that weights the relative importance of each indicator (i.e., multicriteria decision analysis). The whole process of mapping and ranking wetlands in the Manawatu–Wanganui region took only 6 weeks. The rapid methodology means that consistent wetland inventories and ranking can now actually be produced at reasonable cost, and conservation resources may therefore be better targeted. With complete inventories and priority lists of wetlands, managers will be able to plan for conservation without having to wait for the collection of detailed biologic information, which may now also be prioritised.     

Modeling wetland loss in coastal Louisiana: Geology,geography, and human modifications

Habitat change in coastal Louisiana from 1955/6 to 1978 was analyzed to determine the influence of geological and man-made changes on landscape patterns within 7.5 min quadrangle maps. Three quantitative analyses were used: principal components anlaysis, multiple regression analysis, and cluster analysis.Regional differences in land loss rates reflect variations in geology and the deltaic growth/decay cycles, man-induced chages in hydrology (principally canal dredging and spoil banking), and land-use changes (principally urbanization and agricultural expansion). The coastal zone is not homogeneous with respect to these variables and the interaction between causal factors leading to wetland loss is therefore locally variable and complex.The relationship between wetland loss, hydrologic changes, and geology can be described with statistically meaningful results, even though these data are insufficient to precisely quantify the relationship. However, these data support the hypothesis that the indirect impacts of man-induced changes (hydrologic and land use) may be as influential as the direct impacts resulting in converting wetlands to open water (canals) or modified (impounded) habitat.Three regions within the Louisiana coastal zone can be defined, based on the potential causal factors used in the analyses. The moderate (mean = 22%) wetland loss rates in region 1 are a result of relatively high canal density and developed area in marshes which overlie sediments of moderate age and depth; local geology acts, in this case, to lessen indirect impacts. On the other hand, wetland loss rates in region 2 are high (mean = 36%), despite fewer man-induced impacts; the potential for increased wetland loss due to both direct and indirect effects of man's activity in these areas is high. Conversely, wetland loss (mean = 20%) in region 3 is apparently least influenced by man's activity in the coastal zone because of sedimentary geology (old, thin sediments), even though these areas have already experienced significant direct habitat alteration and wetland loss.     

Monitoring Environmental Changes in the Mediterranean Coastal Landscape: The Case of Cukurova, Turkey

This paper describes a remote sensing approach used to monitor temporal land use/cover (LULC) changes in Cukurova, an extensive coastal plain in the southeast Mediterranean coast of Turkey. The area has varied terrain ranging from low-lying alluvial deposits to rocky hills and mountains characterized by limestone outcrops. The ecological and economic importance of the area can be attributed to the existence of important coastal ecosystems (e.g., wetlands and sand dunes) and a wide range of industries located along the eastern coast. Temporal changes in the coastal landscape between 1984 and 2000 were evaluated using digital interpretation of remotely sensed satellite data. Pairwise comparison methods were used to quantify changes from 1984 to 1993 and 1993 to 2000 using multitemporal Landsat TM and ETM+ images, acquired in 1984, 1993, and 2000, respectively. Total change area was 2448 ha from 1984 to 1993 and increased more than twofold, to 6072 ha from 1993 to 2000. Change trends were determined using the information provided from individual change detection outputs of different periods. The most prominent changes were estimated to have occurred in agriculture, urban, and natural vegetation cover. Agriculture has increasingly grown over marginal areas, whereas urban development occurred at the expense of prime croplands across both time steps.     

Land-cover change in upper Barataria Basin estuary,Louisiana, 1972-1992: increases in Wetland area

The Barataria Basin, Louisiana, USA, is an extensive wetland and coastal estuary system of great economic and intrinsic value. Although high rates of wetland loss along the coastal margin of the Barataria Basin have been well documented, little information exists on whether freshwater wetlands in the upper basin have changed. Our objectives were to quantify land-cover change in the upper basin over 20 years from 1972–1992 and to determine land-cover transition rates among land-cover types. Using 80-m resolution Landsat MSS data from the North American Landscape Characterization (NALC) data archive, we classified images from three time steps (1972, 1985, 1992) into six land-cover types: agriculture, urban, bottomland hardwood forest, swamp forest, freshwater marsh, and open water. Significant changes in land cover occurred within the upper Barataria Basin over the study period. Urban land increased from 8% to 17% of the total upper basin area, primarily due to conversions from agricultural land, and to a lesser degree, bottomland forest. Swamp forest increased from 30% to 41%, associated with conversions from bottomland hardwood forest and freshwater marsh. Overall, bottomland forest decreased 38% and total wetland area increased 21%. Within the upper Barataria, increases in total wetland area may be due to land subsidence. Based on our results, if present trends in the reduction of bottomland forest land cover were to continue, the upper Barataria Basin may have no bottomland hardwood forests left by the year 2025, as it is subjected to multiple stressors both in the higher elevations (from urbanization) and lower elevations (most likely from land subsidence). These results suggest that changes in the upper freshwater portions of coastal estuaries can be large and quite different from patterns observed in the more saline coastal margins.