胶州湾滨海湿地的景观格局变化及环境效应

在湿地景观类型分类基础上,利用RS及GIS技术提取了1986、1995和2010年胶州湾滨海湿地的Landsat卫星假彩色合成影像的空间属性数据,利用斑块动态度、斑块密度指数、景观多样性指数、斑块破碎化指数研究了胶州湾滨海湿地的景观格局变化及累积环境效应。结果表明,1986～2010年胶州湾滨海湿地总面积减少,河流与河口湿地面积稍有增大,潮间带滩涂和潮上带湿地面积和斑块数减小;养殖池面积增大、斑块数增多,盐田面积减小、斑块数基本未变,增加了湿地公园这种新的人工湿地景观类型。期间,湿地的景观斑块密度指数、多样性指数和景观斑块破碎化指数增大了。上述湿地面积和景观格局变化是由围垦、城市化、港口和道路建设、河流径流量和输沙量减少、海岸侵蚀、海水入侵、全球变暖、海面上升等因素引起的,并导致湿地生物多样化水平下降、有害植物入侵、环境净化功能降低、污染和赤潮灾害加重、植被退化演替、渔业资源衰退和湿地生态系统服务价值降低等累积环境效应。为减轻这些不利的累积环境效应,应采取建设湿地自然保护区、控制养殖池和盐田规模、发展工业循环经济和生态农业等措施保护胶州湾滨海湿地。     

Landscape Pattern Changes and Their Environmental Effects of Coastal Wetlands in Jiaozhou Bav

在湿地景观类型分类基础上,利用RS及GIS技术提取了1986、1995和2010年胶州湾滨海湿地的Landsat卫星假彩色合成影像的空间属性数据,利用斑块动态度、斑块密度指数、景观多样性指数、斑块破碎化指数研究了胶州湾滨海湿地的景观格局变化及累积环境效应.结果表明,1986～2010年胶州湾滨海湿地总面积减少,河流与河口湿地面积稍有增大,潮间带滩涂和潮上带湿地面积和斑块数减小;养殖池面积增大、斑块数增多,盐田面积减小、斑块数基本未变,增加了湿地公园这种新的人工湿地景观类型.期间,湿地的景观斑块密度指数、多样性指数和景观斑块破碎化指数增大了.上述湿地面积和景观格局变化是由围垦、城市化、港口和道路建设、河流径流量和输沙量减少、海岸侵蚀、海水入侵、全球变暖、海面上升等因素引起的,并导致湿地生物多样化水平下降、有害植物入侵、环境净化功能降低、污染和赤潮灾害加重、植被退化演替、渔业资源衰退和湿地生态系统服务价值降低等累积环境效应.为减轻这些不利的累积环境效应,应采取建设湿地自然保护区、控制养殖池和盐田规模、发展工业循环经济和生态农业等措施保护胶州湾滨海湿地.     

中国北方滨海湿地退化研究综述

中国北方沿海有入海河口湿地、三角洲湿地、粉砂淤泥质海岸湿地、海湾湿地、砂质海岸湿地、沉积岛屿滩涂湿地和滨海泻湖湿地等类型的滨海湿地约182.33×104hm2。由于受到海岸侵蚀、海面上升、风暴潮、入海河流断流和输沙量减少、气候变化等自然因素和围垦、城市和港口建设、污染、海岸带油气资源开发、在入海河流上中游建设水库拦蓄径流和泥沙等人为因素的影响,中国北方的滨海湿地发生了严重的退化。中国北方滨海湿地的退化表现在物理、化学和生物3个方面。其中物理方面表现为自然湿地面积减小、人工湿地面积增大、湿地景观格局破碎化等,化学方面表现为湿地温室气体排放增加、水体富营养化、潮下带近海湿地赤潮灾害增强、湿地底质和渔获物污染、湿地土壤含盐量变化等,生物方面表现为湿地生物多样性水平下降、自然湿地净初级生产力降低、潮间带滩涂湿地和潮下带近海湿地渔获量减小、自然湿地植被退化演替等。     

华南西部滨海湿地调查及主要成果

通过遥感、单波束测量、地质取样、海水取样、钻探、地下水采集与监测等多种调查手段及工作方法,首次在我国华南西部开展1∶10万滨海湿地地质调查与生态环境评价工作,对滨海湿地类型及分布、滨海海域地形地貌、沉积物环境质量、海水环境质量、生态地质演化、地下水化学要素进行综合分析与研究。项目系统查明了该区滨海湿地类型、分布、生态环境现状及其主要影响因素,对湿地生态地质环境质量进行了综合评价,构建了华南西部滨海湿地地质调查技术方法体系和生态地质环境综合评价体系,提出了滨海湿地保护和恢复的建议,为后续我国南方滨海湿地调查提供了示范。     

黄河三角洲滨海湿地健康条件评价

以黄河三角洲滨海湿地系统为研究对象,基于描述滨海湿地健康条件的4项功能,充分考虑滨海湿地生态地质环境系统的特征及其健康响应因素,建立了黄河三角洲滨海湿地健康条件评价的概念模型和指标体系。以统计监测和遥感数据为基础,采用RS和GIS技术,通过栅格化实现分区评价及其结果的优化整合,探讨了黄河三角洲滨海湿地健康的时空分布规律。结果显示：黄河三角洲滨海湿地现状健康条件处于健康的占14.2%,亚健康的占61.9%,一般病态的占23.9%;近期（2010－2015年）,河口三角洲湿地生境质量会逐步改善,向健康方向发展,而北部和南部部分滩涂区及神仙沟流路等局部地区在自然和人为因素的共同作用下,环境质量会有一定的降低;影响黄河三角洲滨海湿地健康条件的主要因素是全球气候变化背景下的区域水循环关键过程及其时空变化、湿地开发等人类负面干扰和黄河下游生态调度。应继续加大黄河下游生态调度的力度、积极实施生态修复工程,以促进黄河三角洲滨海湿地持续健康发展。     

黄河三角洲进积与滨海湿地地质环境演替模式

本文通过对黄河三角洲5个钻孔岩芯的沉积学观测、微古分析、14C测年,同时结合历史记录及遥感资料,分析了本区末次冰后期以来的沉积序列,重建了近10ka以来古环境演变过程,分析了古环境演化对滨海湿地演替的控制作用。本文着重讨论了黄河三角洲进积与湿地形成演替规律,总结了从水生系统、浅海湿地系统、潮滩湿地直至上三角洲平原湿地向陆地生态系统的演替模式。同时通过对现代黄河三角洲与老黄河三角洲演化模式进行对比,提出气候变化、人类活动会加速和改变湿地地质环境演替进程和方向的一般规律。笔者等还进一步提出,由于人类活动的影响,1855年之后湿地演替速率明显加快,约达8~33倍。古环境的重建与滨海湿地响应机制研究可更清楚地理解湿地如何对未来环境变化进行响应,包括海平面上升,从而为滨海湿地保护与管理实践活动提供科学导向。     

现代黄河三角洲滨海湿地生态水文环境脆弱性

受大气降水、黄河水位断流、风暴潮和人类工程活动等因素影响,现代黄河三角洲滨海湿地生态水文环境极其脆弱和敏感。本文运用地下水数值模拟方法,通过构建滨海湿地水文模型,以氯离子作为模拟因子,预测滨海湿地地下水趋势性变化。计算结果显示,湿地水位和盐度对湿地生长和发育起控制作用;黄河持续断流和强烈风暴潮对湿地水质影响明显;当风暴潮引起增水幅度超过正常潮高的2.4m,会造成沿海低地特别是北部未受防潮大坝保护的滨海湿地淹没。     

基于RS和GIS的鸭绿江口滨海湿地分类及变化

遥感技术是湿地资源调查与监测的有效手段之一。以遥感影像资料为基础,结合GIS技术对鸭绿江口滨海湿地进行定量化研究,查明湿地的类型分布、面积,分析其1989-2000年期间土地利用的变化。结果表明：虾田、居民地、滩涂面积增加;芦苇沼泽、水田、浅海水域面积减少;湿地生态环境遭到破坏。这些主要是由城市扩张和经济增长所致。天然湿地的减少,使依赖于湿地生存的动、植物种类大大减少。为保护湿地生态环境,应严禁毁苇开荒,逐步退耕还苇,加强管理,合理开发利用,使本区可持续发展。     

黄河三角洲滨海湿地健康条件评价概念模型

滨海湿地健康与生物学特征主要取决于区域上的水文与盐度体制以及景观尺度上的土地利用现状。然而,由于滨海湿地条件评价的指标和标准并不十分清楚,因此,对滨海湿地系统条件进行评价,目前仍是环境科学的难点。中国地质调查局（CGS）青岛海洋地质研究所与美国地质调查局湿地研究中心合作先后为美国密西西比河下游生态环境及中国黄河三角洲（YRD）滨海湿地评价建立了概念模型。本文将陈述YRD湿地评价的概念模型。此模型的建立在于确定滨海湿地当前的条件和随时间改善或退化的过程,以及确定优先管理的区域。CGS项目之所以选取YRD作为滨海湿地的研究对象主要是因为它具有重要的生态意义。由于上游来水减少或黄河断流,该区湿地生境十分脆弱。本文提出此概念模型可为今后湿地条件评价指标确定、调查研究活动和数据采集提供指导。通过该模型的构建,使环境变化可用具体指标来度量,从而服务于滨海湿地生态系统的保护与管理活动。     

云南：立法保护湿地资源

云南省人大常委会近日出台条例,对昭通大山包自然区湿地资源实行有效保护和合理开发利用。大山包自然区位于滇东北距昭通市区80余公里处,3000公顷面积内分布有数千亩高山湖泊、19万亩高山草甸、19处适宜涉禽鸟类栖息觅食的高原湿地,被列入国际重要湿地名单。条例规定,建立大山包湿地专门保护机构,制定整体规划和具体实施办法。加大湿地保护力度,有计划地实施退耕还林还草,开展地质灾害、     

大连滨海湿地景观格局变化及其驱动机制

以2000年和2006年TM卫星影像为主要数据源,配合其它非遥感数据,在遥感与地理信息系统技术支持下,运用景观生态学原理,选取反映景观空间结构和景观异质性的指数,对大连地区湿地的整体景观格局和类型景观格局及其动态变化进行定量分析.结果表明:6年间,大连湿地面积减少了97.62 km2;整体景观多样性指数和均匀度指数降低,优势度指数增加;各类景观格局时间序列上也存在明显差异性变化.湿地景观格局指数的变化, 反映了移山填海工业园区的扩大及养殖业的大力发展等人为活动对景观格局的深刻影响.人为活动已成为大连市湿地景观格局变化的主要驱动因子.     

山东省湿地类型及湿地环境地质问题分析

山东省湿地资源丰富,可分为自然湿地和人工湿地2类,自然湿地包括湖泊、海岸、沼泽、河口湾湿地,人工湿地主要为水稻田、水库、池塘湿地等,湿地面积约为1．71万km^2。该文分析研究了山东省的湿地环境地质问题,并提出了工程措施和非工程措施2种防治措施。     

Consequences of Climate Change on the Ecogeomorphology of Coastal Wetlands

Climate impacts on coastal and estuarine systems take many forms and are dependent on the local conditions, including those set by humans. We use a biocomplexity framework to provide a perspective of the consequences of climate change for coastal wetland ecogeomorphology. We concentrate on three dimensions of climate change affects on ecogeomorphology: sea level rise, changes in storm frequency and intensity, and changes in freshwater, sediment, and nutrient inputs. While sea level rise, storms, sedimentation, and changing freshwater input can directly impact coastal and estuarine wetlands, biological processes can modify these physical impacts. Geomorphological changes to coastal and estuarine ecosystems can induce complex outcomes for the biota that are not themselves intuitively obvious because they are mediated by networks of biological interactions. Human impacts on wetlands occur at all scales. At the global scale, humans are altering climate at rapid rates compared to the historical and recent geological record. Climate change can disrupt ecological systems if it occurs at characteristic time scales shorter than ecological system response and causes alterations in ecological function that foster changes in structure or alter functional interactions. Many coastal wetlands can adjust to predicted climate change, but human impacts, in combination with climate change, will significantly affect coastal wetland ecosystems. Management for climate change must strike a balance between that which allows pulsing of materials and energy to the ecosystems and promotes ecosystem goods and services, while protecting human structures and activities. Science-based management depends on a multi-scale understanding of these biocomplex wetland systems. Causation is often associated with multiple factors, considerable variability, feedbacks, and interferences. The impacts of climate change can be detected through monitoring and assessment of historical or geological records. Attribution can be inferred through these in conjunction with experimentation and modeling. A significant challenge to allow wise management of coastal wetlands is to develop observing systems that act at appropriate scales to detect global climate change and its effects in the context of the various local and smaller scale effects.     

A Landscape-Scale Assessment of Above- and Belowground Primary Production in Coastal Wetlands: Implications for Climate Change-Induced Community Shifts

Above- and belowground production in coastal wetlands are important contributors to carbon accumulation and ecosystem sustainability. As sea level rises, we can expect shifts to more salt-tolerant communities, which may alter these ecosystem functions and services. Although the direct influence of salinity on species-level primary production has been documented, we lack an understanding of the landscape-level response of coastal wetlands to increasing salinity. What are the indirect effects of sea-level rise, i.e., how does primary production vary across a landscape gradient of increasing salinity that incorporates changes in wetland type? This is the first study to measure both above- and belowground production in four wetland types that span an entire coastal gradient from fresh to saline wetlands. We hypothesized that increasing salinity would limit rates of primary production, and saline marshes would have lower rates of above- and belowground production than fresher marshes. However, along the Northern Gulf of Mexico Coast in Louisiana, USA, we found that aboveground production was highest in brackish marshes, compared with fresh, intermediate, and saline marshes, and belowground production was similar among all wetland types along the salinity gradient. Multiple regression analysis indicated that salinity was the only significant predictor of production, and its influence was dependent upon wetland type. We concluded that (1) salinity had a negative effect on production within wetland type, and this relationship was strongest in the fresh marsh (0–2 PSU) and (2) along the overall landscape gradient, production was maintained by mechanisms at the scale of wetland type, which were likely related to plant energetics. Regardless of wetland type, we found that belowground production was significantly greater than aboveground production. Additionally, inter-annual variation, associated with severe drought conditions, was observed exclusively for belowground production, which may be a more sensitive indicator of ecosystem health than aboveground production.     

Tampa Bay Coastal Wetlands: Nineteenth to Twentieth Century Tidal Marsh-to-Mangrove Conversion

Currently, mangroves dominate the tidal wetlands of Tampa Bay, Florida, but an examination of historic navigation charts revealed dominance of tidal marshes with a mangrove fringe in the 1870s. This study's objective was to conduct a new assessment of wetland change in Tampa Bay by digitizing nineteenth century topographic and public land surveys and comparing these to modern coastal features at four locations. We differentiate between wetland loss, wetland gain through marine transgression, and a wetland conversion from marsh to mangrove. Wetland loss was greatest at study sites to the east and north. Expansion of the intertidal zone through marine transgression, across adjacent low-lying land, was documented primarily near the mouth of the bay. Generally, the bay-wide marsh-to-mangrove ratio reversed from 86:14 to 25:75 in 125?years. Conversion of marsh to mangrove wetlands averaged 72?% at the four sites, ranging from 52?% at Old Tampa Bay to 95?% at Feather Sound. In addition to latitudinal influences, intact wetlands and areas with greater freshwater influence exhibited a lower rate of marsh-to-mangrove conversion. Two sources for nineteenth century coastal landscape were in close agreement, providing an unprecedented view of historic conditions in Tampa Bay.     

Integrating Successional Ecology and the Delta Lobe Cycle in Wetland Research and Restoration

Inactive deltas are more extensive than active deltas in most deltaic landscapes; thus, the subsurface generally is dominated by mineral sediments that rapidly accreted at different times, whereas the landscape at any one time generally is dominated by ephemeral emergent wetlands that are slowly accreting via vegetative growth. Subsidence is slow enough in most deltas that emergent wetlands, although ephemeral, can persist for millennia but accelerating global sea level rise probably will slow wetland creation in active deltas and accelerate the loss of existing wetlands in inactive deltas this century worldwide. A recent publication created confusion regarding the effects of river management on coastal Louisiana, where spatially variable subsidence is great enough in some areas to mimic extremely rapid sea level rise. I show how integrating Successional Ecology with the Delta Lobe Cycle, and correcting some omissions and errors in recent publications, clarifies the effects of river management in coastal Louisiana and provides a framework for predicting deltaic landscape dynamics worldwide. Successional Ecology provides a framework for understanding changes in natural and managed environments worldwide, whereas the Delta Lobe Cycle provides a framework for understanding river-dominated deltas worldwide. Sediment diversions are a form of river management that removes artificial barriers to river flow and are designed to mimic hydrologic conditions during the active delta stage of the Delta Lobe Cycle by focusing rapid mineral sedimentation in open water and thus creating new emergent wetlands. Freshwater diversions are another form of river management that also removes artificial barriers to river flow but are designed to mimic hydrologic conditions during the inactive stages of the Delta Lobe Cycle by reducing salinity stress over large areas of emergent wetlands and thus promoting marsh vertical accretion via vegetative growth. The Delta Lobe Cycle and both types of river diversions also create salinity gradients that simultaneously increase the sensitivity of emergent wetlands to disturbance while increasing the ability of emergent wetlands to recover from disturbance. Freshwater diversions only slow the loss of existing wetlands because the natural Delta Lobe Cycle, artificial channels that increase salinity stress, artificial ridges that increase flooding stress, and repeated disturbances eventually will cause vertical accretion via vegetative growth to become inadequate. Formally integrating these concepts might advance research and restoration in deltaic landscapes worldwide especially in the majority of deltas where inactive deltas are more extensive than active deltas.     

Managed Retreat of Saline Coastal Wetlands: Challenges and Opportunities Identified from the Hunter River Estuary,Australia

We analyse the potential impacts of sea-level rise on the management of saline coastal wetlands in the Hunter River estuary, NSW, Australia. We model two management options: leaving all floodgates open, facilitating retreat of mangrove and saltmarsh into low-lying coastal lands; and leaving floodgates closed. For both management options we modelled the potential extent of saline coastal wetland to 2100 under a low sea-level rise scenario (based on 5 % minima of SRES B1 emissions scenario) and a high sea-level rise scenario (based on 95 % maxima of SRES A1FI emissions scenario). In both instances we quantified the carbon burial benefits associated with those actions. Using a dynamic elevation model, which factored in the accretion and vertical elevation responses of mangrove and saltmarsh to rising sea levels, we projected the distribution of saline coastal wetlands, and estimated the volume of sediment and carbon burial across the estuary under each scenario. We found that the management of floodgates is the primary determinant of potential saline coastal wetland extent to 2100, with only 33 % of the potential wetland area remaining under the high sea-level rise scenario, with floodgates closed, and with a 127 % expansion of potential wetland extent with floodgates open and levees breached. Carbon burial was an additional benefit of accommodating landward retreat of wetlands, with an additional 280,000 tonnes of carbon buried under the high sea-level rise scenario with floodgates open (775,075 tonnes with floodgates open and 490,280 tonnes with floodgates closed). Nearly all of the Hunter Wetlands National Park, a Ramsar wetland, will be lost under the high sea-level rise scenario, while there is potential for expansion of the wetland area by 35 % under the low sea-level rise scenario, regardless of floodgate management. We recommend that National Parks, Reserves, Ramsar sites and other static conservation mechanisms employed to protect significant coastal wetlands must begin to employ dynamic buffers to accommodate sea-level rise change impacts, which will likely require land purchase or other agreements with private landholders. The costs of facilitating adaptation may be offset by carbon sequestration gains.     

Contribution of Mangroves and Salt Marshes to Nature-Based Mitigation of Coastal Flood Risks in Major Deltas of the World

Nature-based solutions are rapidly gaining interest in the face of global change and increasing flood risks. While assessments of flood risk mitigation by coastal ecosystems are mainly restricted to local scales, our study assesses the contribution of salt marshes and mangroves to nature-based storm surge mitigation in 11 large deltas around the world. We present a relatively simple GIS model that, based on globally available input data, provides an estimation of the tidal wetland’s capacity of risk mitigation at a regional scale. It shows the high potential of nature-based solutions, as tidal wetlands, to provide storm surge mitigation to more than 80% of the flood-exposed land area for 4 of the 11 deltas and to more than 70% of the flood-exposed population for 3 deltas. The magnitude of the nature-based mitigation, estimated as the length of the storm surge pathway crossing through tidal wetlands, was found to be significantly correlated to the total wetland area within a delta. This highlights the importance of conserving extensive continuous tidal wetlands as a nature-based approach to mitigate flood risks. Our analysis further reveals that deltas with limited historical wetland reclamation and therefore large remaining wetlands, such as the Mississippi, the Niger, and part of the Ganges-Brahmaputra deltas, benefit from investing in the conservation of their vast wetlands, while deltas with extensive historical wetland reclamation, such as the Yangtze and Rhine deltas, may improve the sustainability of flood protection programs by combining existing hard engineering with new nature-based solutions through restoration of former wetlands.