黄土丘陵区坡面整地和植被耦合下的土壤水分特征

水分是干旱半干旱地区植被恢复的主要环境制约因子。在黄土高原小流域,合理整地能够有效截留降雨补给土壤水,进而促进植被恢复。选择地处甘肃定西的半干旱黄土小流域为研究区,基于野外实测数据,分析不同植被和整地方式(柠条水平阶、山杏水平沟、侧柏反坡台,油松反坡台)综合影响下的土壤水分特征。采用最优分割法将不同整地方式土壤水分垂直层次划分为活跃层,次活跃层和相对稳定层。结果表明:生长季不同整地方式土壤水分的变化与降水量的变化密切相关,不同月份以及不同深度各整地方式土壤水分之间差异显著(P0.05)。根据土壤水分垂直变化特征,山杏水平沟水分活跃层与次活跃层为0—80cm,其深度范围均大于其他3种整地方式,而柠条水平阶土壤水分均在30 cm以下较为稳定,其深度范围均小于其他3种整地方式。不同整地方式土壤水分含量具体表现为:山杏水平沟侧柏反坡台柠条水平阶油松反坡台。     

Influence of spatially dependent,modeled soil carbon emission factors on life‐cycle greenhouse gas emissions of corn and cellulosic ethanol

Converting land to biofuel feedstock production incurs changes in soil organic carbon (SOC) that can influence biofuel life‐cycle greenhouse gas (GHG) emissions. Estimates of these land use change (LUC) and life‐cycle GHG emissions affect biofuels' attractiveness and eligibility under a number of renewable fuel policies in the USA and abroad. Modeling was used to refine the spatial resolution and depth extent of domestic estimates of SOC change for land (cropland, cropland pasture, grassland, and forest) conversion scenarios to biofuel crops (corn, corn stover, switchgrass, Miscanthus, poplar, and willow) at the county level in the USA. Results show that in most regions, conversions from cropland and cropland pasture to biofuel crops led to neutral or small levels of SOC sequestration, while conversion of grassland and forest generally caused net SOC loss. SOC change results were incorporated into the Greenhouse Gases, Regulated Emissions, and Energy use in Transportation (GREET) model to assess their influence on life‐cycle GHG emissions of corn and cellulosic ethanol. Total LUC GHG emissions (g CO₂eq MJ^?1) were 2.1–9.3 for corn‐, ?0.7 for corn stover‐, ?3.4 to 12.9 for switchgrass‐, and ?20.1 to ?6.2 for Miscanthus ethanol; these varied with SOC modeling assumptions applied. Extending the soil depth from 30 to 100 cm affected spatially explicit SOC change and overall LUC GHG emissions; however, the influence on LUC GHG emission estimates was less significant in corn and corn stover than cellulosic feedstocks. Total life‐cycle GHG emissions (g CO₂eq MJ^?1, 100 cm) were estimated to be 59–66 for corn ethanol, 14 for stover ethanol, 18–26 for switchgrass ethanol, and ?7 to ?0.6 for Miscanthus ethanol. The LUC GHG emissions associated with poplar‐ and willow‐derived ethanol may be higher than that for switchgrass ethanol due to lower biomass yield.     

基于TM的渤海海岸带1988～2000年生态环境变化

海岸带作为海陆之间的过渡地带,是全球生态环境最为复杂和特殊之处。研究海岸带土地利用变化对于了解该区域生态环境演变具有重要意义。利用1988和2000年的Landsat-TM数据,在GIS技术支持下,通过一系列空间分析,得到渤海海岸带土地利用/土地覆盖变化,结合社会经济统计资料分析该区域生态环境的动态变化情况及其驱动因素。结果表明,1988~2000年,由于渤海海岸带社会经济的快速发展,海岸带土地利用格局发生了巨大的变化。耕地大面积减少,城乡工矿用地、养殖池塘、盐田急剧扩张;林地、湿地等具有重要生态价值的土地类型面积显著下降。表明强烈的人类活动已经使自然生态系统受到破坏,渤海海岸带生态环境质量总体上呈现下降趋势。     

2030年闽三角城市群土地利用变化对生态系统水源涵养服务的影响

生态系统水源涵养服务作为水资源得以持续的基础和保障,正持续遭受着人类活动的干扰和影响,土地利用变化作为主要的方式之一,对水源涵养的影响广泛而且深远。运用InVEST模型模拟了闽三角城市群2015年和2030年的水源涵养情景,发现到2030年闽三角城市群区域内水源涵养量总体会下降0.24×10⁸ m³;对比发现：土地利用变化对水源涵养的影响主要主要表现在变化面积、变化方向、作用强度以及面积补偿作用四个方面。首先面积变化方面,水源涵养量同用地类型的面积大小正相关,但二者的变化量并不正相关;其次变化方向方面,相比变化为城市生态系统和水域生态系统而言,变化为自然生态系统和农业生态系统的土地利用变化更有利于生态系统水源涵养;再次,土地利用变化对水源涵养产生作用的强度由强及弱以此为林地、其他土地、草地、农田、建设用地、水域及滩涂;最后,面积变化后的补偿作用方面,由于不同用地类型水源涵养能力和面积变化量的差异,由农田、林地、草地及其他土地面积下降导致的水源涵养量损失并不能通过建设用地、水域及滩涂用地类型面积的增加得以完全补偿。     

土地利用变化对海南土壤水源涵养功能的影响

热带地区已有大量原始林转变为其他土地利用类型,影响了陆地生态系统的水源涵养功能.为了明确热带原始林转变为其他土地类型对土壤水源涵养功能的影响,在海南中部山区选择4种典型土地利用类型,包括林龄大于100年的原始林(VF)、10年生次生林(SF)、12年生槟榔林(AF)和35年生橡胶林(RF),评估土地利用变化对土壤持水性能和水源涵养功能指数(SWI)的影响.结果表明: 与原始林相比,表层土壤(0～10 cm)中,其他土地类型土壤持水性能指标均降低,12年槟榔林各土层指标均最低.土壤含水量和最大持水量与植被郁闭度、土壤有机质和土壤容重显著相关,表明郁闭度、土壤有机质和紧实度的改变是土壤持水性能变化的重要原因.与原始林相比,次生林、槟榔林和橡胶林土壤水源涵养功能分别减少27.7%、54.3%和11.5%,不同土层的差异各异,橡胶林仅表层土壤水源涵养功能显著降低.植被郁闭度、土壤有机质和土壤容重可解释土壤水源涵养功能变量的83.3%.土地利用转变显著改变了土壤持水性能和土壤水源涵养功能,相比12年槟榔林,35年橡胶林能更好地保持土壤水分,土地管理中增加土壤有机质和减少土壤紧实度可改善土壤持水性能及水源涵养功能.     

Trade‐offs between land and water requirements for large‐scale bioenergy production

Bioenergy is expected to play an important role in the future energy mix as it can substitute fossil fuels and contribute to climate change mitigation. However, large‐scale bioenergy cultivation may put substantial pressure on land and water resources. While irrigated bioenergy production can reduce the pressure on land due to higher yields, associated irrigation water requirements may lead to degradation of freshwater ecosystems and to conflicts with other potential users. In this article, we investigate the trade‐offs between land and water requirements of large‐scale bioenergy production. To this end, we adopt an exogenous demand trajectory for bioenergy from dedicated energy crops, targeted at limiting greenhouse gas emissions in the energy sector to 1100 Gt carbon dioxide equivalent until 2095. We then use the spatially explicit global land‐ and water‐use allocation model MAgPIE to project the implications of this bioenergy target for global land and water resources. We find that producing 300 EJ yr^?1 of bioenergy in 2095 from dedicated bioenergy crops is likely to double agricultural water withdrawals if no explicit water protection policies are implemented. Since current human water withdrawals are dominated by agriculture and already lead to ecosystem degradation and biodiversity loss, such a doubling will pose a severe threat to freshwater ecosystems. If irrigated bioenergy production is prohibited to prevent negative impacts of bioenergy cultivation on water resources, bioenergy land requirements for meeting a 300 EJ yr^?1 bioenergy target increase substantially (+ 41%) – mainly at the expense of pasture areas and tropical forests. Thus, avoiding negative environmental impacts of large‐scale bioenergy production will require policies that balance associated water and land requirements.     

Projecting future grassland productivity to assess the sustainability of potential biofuel feedstock areas in the Greater Platte River Basin

This study projects future (e.g., 2050 and 2099) grassland productivities in the Greater Platte River Basin (GPRB) using ecosystem performance (EP, a surrogate for measuring ecosystem productivity) models and future climate projections. The EP models developed from a previous study were based on the satellite vegetation index, site geophysical and biophysical features, and weather and climate drivers. The future climate data used in this study were derived from the National Center for Atmospheric Research Community Climate System Model 3.0 ‘SRES A1B’ (a ‘middle’ emissions path). The main objective of this study is to assess the future sustainability of the potential biofuel feedstock areas identified in a previous study. Results show that the potential biofuel feedstock areas (the more mesic eastern part of the GPRB) will remain productive (i.e., aboveground grassland biomass productivity >2750 kg ha^?1 year^?1) with a slight increasing trend in the future. The spatially averaged EPs for these areas are 3519, 3432, 3557, 3605, 3752, and 3583 kg ha^?1 year^?1 for current site potential (2000–2008 average), 2020, 2030, 2040, 2050, and 2099, respectively. Therefore, the identified potential biofuel feedstock areas will likely continue to be sustainable for future biofuel development. On the other hand, grasslands identified as having no biofuel potential in the drier western part of the GPRB would be expected to stay unproductive in the future (spatially averaged EPs are 1822, 1691, 1896, 2306, 1994, and 2169 kg ha^?1 year^?1 for site potential, 2020, 2030, 2040, 2050, and 2099). These areas should continue to be unsuitable for biofuel feedstock development in the future. These future grassland productivity estimation maps can help land managers to understand and adapt to the expected changes in future EP in the GPRB and to assess the future sustainability and feasibility of potential biofuel feedstock areas.     

基于RS和GIS的开封市土地覆盖分形

以RS和GIS为技术手段,利用开封市0.61m空间分辨率的QuickBird卫星遥感数据,采用分形几何方法研究了斑块的面积效应和覆盖类型分形的关系,并对覆盖类型的分形特征差异等进行了分析。结果表明,开封市防护林地和农田的平均斑块面积较大,分维数也较大,而水体的分维数较小,说明防护林和农田斑块的边界结构特征比水体更为复杂。斑块的分维值具有尺度依赖性,同一类型中大的斑块往往具有较大的分维值,其原因是大斑块经常出现不同类型的斑块相互嵌套,小斑块则很少出现甚至不出现这种现象。     

开封地区不同土地利用方式农田杂草群落结构及动态

2005年春、秋两季对开封地区不同土地利用方式小麦-玉米、小麦-大豆轮作地,葡萄地,弃耕地中杂草进行调查,统计分析各杂草群落中物种相似系数、物种相对多度分布、功能群相对多度和生物多样性。杂草功能群分为单子叶短期生植物（MA）、双子叶短期生植物（DA）、单子叶多年生植物（MP）及双子叶多年生植物（DP）4个功能类群。调查共记录杂草种类71种,隶属27个科;春季51种、共同种7个,秋季36种、共同种8个。不同土地利用方式杂草群落相似系数春季各群落间0．3～0．5,秋季玉米地-大豆地、秋葡萄地-弃耕地最高,分别是0．73和0．70;季节间小麦地与秋季各杂草群落间相似系数小于0．1。春、秋季弃耕地物种-相对多度分布曲线下降缓慢,常见种和偶见种多、相对多度分配分别占61．32％和47．09％;小麦地、玉米地、大豆地和葡萄地优势种突出。春季DA功能群占优势,小麦地高达81．06％;MP功能群较少,小麦地缺少MP。秋季玉米地和大豆地杂草功能群分布较均衡,葡萄地以DA和MP为主、分别为42．34％和42．64％;弃耕地MA、DA和MP平均,为33．63、31．07和30．25％。多样性指数为春、秋季弃耕地最高1．76和1．72,玉米、大豆地次之为1．55和1．52,春、秋葡萄地1．49、1．30,小麦地最低1．12。结论：不同土地利用方式杂草群落种群构成不同,功能群相对多度分配格局以免耕农田玉米地、大豆地和葡萄地杂草功能群分布均衡;功能群季节变化明显,趋势为MP上升,DA下降。不同土地利用方式土地多样性等级为小麦地〈葡萄地〈大豆地和玉米地〈弃耕地。     

城市生态用地分类及其规划的一般原则

城市生态用地的规划布局是城市规划的难点之一,也是急待解决的问题.本文根据城市生态系统的特点,给出了城市生态用地定义,指出城市生态用地同时具有自然属性和社会属性,依据这个特点,将城市生态用地划分为服务型生态用地和功能型生态用地两大类型,并结合具体的城市生态规划对各种类型的生态用地规划进行了定性分析.