基于土壤水分平衡原理的毛乌素沙地草地种植咨询系统

本研究初步建立了基于土壤水分平衡原理的毛乌素沙地草地种植咨询系统“ASSG”，该系统用于进行毛乌素地区沙地草地利用和种植管理咨询，并可进行更新知识库和存储有关咨询结果的操作。该系统适用于田间工作者、农场管理者、有关科研人员以及任何对生态科学和自然资源管理感兴趣者。 在文中描述了该咨询系统的开发过程，即系统的需求分析、设计、实现和运行，该系统实现了专家系统和仿真模型的结合，该模型即基于水分平衡的最佳植被覆盖率模型，有如下初步结论产生：土壤水分的平衡随植被覆盖率变化的情况（上升或下降）取决于立地条件的差异，笼统地讲“植被覆盖率越高越好”或“植被覆盖率一概不宜太高”未免失之偏颇。 在解决复杂的生态学问题时人工智能／专家系统技术的应用以及在定性模型和方法（如专家系统）的应用中使用定量模型（如仿真模型）正处于发展之中，本系统的实现是应用专家系统与仿真模型结合的方法解决实际生态学问题的又一个例子。

鄂尔多斯高原沙地草地的生态异质性

空间异质性的重要性在于其在自然生态系统中的普遍性和它所引起的生态学效应。空间异质性不仅在生态学理论中占有重要位置，而且也是生态系统管理和景观规划等实践中需要解决的基本问题。本文对鄂尔多斯高原(37038，～40052'N，106027'～111028'E)沙地草地的主要景观单元一沙地和风蚀沙化梁地植被与土壤的空间异质性格局与动态进行了定量的描述和实验研究。 在鄂尔多斯高原沙地景观中，通过对两条相互垂直的Skm样线上植被盖度、植物物种数的半方差分析和分形分析，揭示了植被的依赖于空间尺度的自相关特征和等级结构;沙地景观植被结构以小尺度空间变异占优势，植被斑块多集中在5-10 m的尺度上。对植被盖度低于20%的流沙斑点或斑块沿样线分布的空隙度分析表明流沙斑点或斑块呈适度聚集的格局。植被盖度和植物物种数与土壤有机碳和全氮含量的空间异质性之间的关系随空间尺度和生境类型的不同而有所不同。对植物群落内风蚀沙化斑块中的植物再生动态和克隆植物沙鞭的克隆生长观测实验表明，克隆植物的存在有利于风蚀沙化斑块的固定，跨越不同斑块边界的克隆植物的生长导致了斑块间的物质能量流动，从而影响了景观空间异质性的动态。 在风蚀沙化梁地中，梁坡处的土壤最为瘠薄，土壤颗粒组成以中细沙为主，这反映了风沙活动在梁坡处形成的沙粒堆积。相应地，梁坡处是以油蒿为优势种的沙生植物群落，与梁顶的典型草原植物（本氏针茅（Stipa bungeana)+百里香（Thymus serpyllum）+冷蒿（Artemisiafrigida））群落截然不同。从梁顶到梁底，植物群落受控于较大尺度上的与地形有关的环境梯度，因而其在较大尺度上的空间异质性占优势。

浑善达克退化生态系统恢复研究

　　浑善达克沙地是我国四大沙地之一，地处北方干旱半干旱区，为草原区向荒漠区过渡的地带。长期以来，由于人类不合理的生产活动，加上这里脆弱的生态环境，已引起了严重的土地退化问题：流动沙丘面积由1950s年占沙地总面积的2%增加到1990s的近50%。因此浑善达克沙地成为我国研究土地退化、防治沙尘暴的重点地区，本文从自然科学和人文科学相结合的角度出发，对浑善达克沙地草地退化原因、自然恢复潜力、恢复过程、适宜物种选择，以及社区生存、生产等方面进行了综合研究，得出以下主要结论： 　　 1) 浑善达克沙地土壤种子库中含有大量的种子，在退化草地自然恢复中表现出极大的潜力。这些种子在摆脱人和牲畜干扰的前提下，可以萌发、定居并形成植物群落，使退化草地恢复;当地表达到一定程度的植被覆盖，可有效减少沙尘暴的危害。土壤种子库中的植物种类与地上植被有极显著的相似性(P<0.05)，这是地上植被形成稳定群落的基础。种子库中的物种组成影响植被恢复演替的进程;反之，恢复演替也制约着种子库组成和幼苗建立。 　　2)退化沙地草地围封后，对不同恢复阶段草地的群落学调查表明，该地区自然恢复过程大致分为3个阶段：围封2年的恢复早期，流动沙丘向半固定沙丘转变;围封3-5年的恢复中期，半固定沙丘向固定沙丘转变;围封6年后的恢复后期，为固定沙丘稳定发展阶段。根据生活型及植物种类随恢复演替的变化规律，浑善达克沙地植被演替的总体趋势可归纳为：沙米 (Agriophyllum squarrosum)+ 雾冰藜(Bassia dasyphylla)群落→黄柳(Salix gordejevii)+ 冰草(Agropyron cristatum)群落→褐沙蒿(Artemisia intramongolica) + 冰草群落→沙地榆(Ulmus pumila var. sabulosa)疏林+冰草群落。在围封禁牧下，浑善达克退化沙地草地在较短时间内实现自然恢复，因此制约退化草地恢复演替的关键因素主要是人为和牲畜的干扰，只要排除了这种干扰因素，浑善达克大面积的退化沙地草地完全能够借助自然力实现生态恢复。 　　3) 浑善达克沙地3种生境下84种植物叶片渗透势值和含水量，表现出不同功能型上的差异。总体变化趋势为： 深根系 > 浅根系;灌木 > 乔木 > 草本;分布在湿地和丘间低地的植物叶片渗透势和含水量较高，而生长在沙丘上的植物叶片渗透势较低，需要有发达的根系吸收土壤深层的水。不同植物具有独特的水分利用特性，使它们能共存于同一生态系统中。这些不同植物功能型表现出的植物水分生理生态特性，表明浑善达克天然分布的植物群落发育有完善的利用水资源的能力，能够保证在很大降水波动条件下分布有丰富的植物群落和较高的生物生产力，构成该特殊类型生态系统很强的恢复潜力。另外，浑善达克沙地沙丘的存在是该类生态系统恢复弹性较高的另一重要原因。 　　4)本地种与引入种在生理生态上表现出不同的适应能力。在相似的太阳辐射和叶片温度下，引入种旱柳的叶片水势较高，而净光合速率、气孔导度、水分利用效率则较低。这表明它的光合潜能在改变环境中没有正常发挥。同时，引入种较低的最大光化学效率进一步表明它抵抗环境胁迫的能力较低。当土壤水分可利用程度降低而导致水分竞争时，引入种很可能在竞争中被淘汰。因此，在生态恢复中，应尽量避免引入外来种，大量使用本地种。 　　5) 生态恢复不仅是自然科学问题，更重要的是社会经济问题。为了充分认识当地社区的参与对生态恢复的作用，在实验过程中，调查了当地居民自本实验开展以来的思想观念、经济收入和生产效益等变化。在生态恢复中当地社区的积极参与是保证恢复成功与否的关键因素。从发挥“自然力” 和“以人为本”的指导思想出发，在生态恢复中应注重充分利用自然的力量;在管理方面，要以解决社区居民的生产生活实际需求为目标。只有这样，才能保证生态、社会和经济可持续发展。

克隆整合与植物对沙地生境的适应－毛乌素沙地的案例

我国是受荒漠化影响最为严重的国家之一。半干旱区和干燥的亚湿润区分布着大面积沙地，这些沙地是我国荒漠化土地的集中分布区和的主要的潜在发生区，也是重点治理区。在这些地区进行生态建设和生态恢复的首要任务是植被的恢复与重建。用于植被恢复和重建的植物种，必需能够适应沙地特殊的生态环境。 克隆植物是一个独特的植物类群，它广泛的分布于各种生态系统中。在长期的进化过程中，克隆植物形成了有效利用异质性资源以及克服（忍耐或逃避）局部不利环境条件的生态适应对策―克隆整合。位于鄂尔多斯高原的毛乌素沙地是我国的四大沙地之一，其生态环境的特点具备我国沙地生境的共性－干旱、土壤贫瘠、频繁的风沙活动以及异质性。在毛乌素沙地中，克隆植物广泛分布。本文以毛乌素沙地为案例研究的背景，以该区几种重要的克隆植物为研究对象，以该区主要的生态环境特点为处理因素，从不同层面来观察克隆整合对这些植物适应沙地环境的作用。 高度异质性的水分分布格局是该区的关键生态因子之一。水分传输可以帮助克隆植物利用不同斑块内的水分资源。在一个野外实验中，采用酸性品红染色喂饲的方法，研究了根茎型草本克隆植物沙鞭和根茎型克隆半灌木羊柴的克隆内水分传播格局。沙鞭克隆内的水分传输速度和强度都高于羊柴。这可能是沙鞭能够占据大面积生境的原因之一。此外，克隆植物分株间资源的传递是通过贯通的维管束进行的。水分可以在观察的沙鞭克隆片断内畅通无阻的传输，但在羊柴克隆内的传输受到限制。这可能与二者维管束结构的不同有关。 沙埋是该区植物经常遭遇的生态事件。本文研究了克隆整合在羊柴遭受空间异质性沙埋过程中的作用。结果表明，轻微程度的沙埋可以促进羊柴的生长和生物量积累;高强度的沙埋会削弱羊柴的生长和生物量积累，甚至会致死。克隆整合可以帮助羊柴抵抗空间异质性沙埋，尤其当沙埋的强度增加时，这种作用表现的更明显。实际上，沙埋的发生是逐渐进行的，即同时具有时间异质性。本文通过野外实验观察了沙鞭在时空异质性沙埋条件下的响应格局以及克隆整合的作用。研究表明，长时间间隔的沙埋促进沙鞭的生物量积累，克隆整合可以帮助沙鞭抵抗频繁发生的沙埋事件。此外，通过Meta-analysis方法综合了分布在沙地中的根茎型克隆植物对沙埋的响应格局的案例研究。结果表明，轻微的沙埋能够促进根茎型克隆植物的生物量积累，高强度的沙埋对这些植物是一种生态胁迫，克隆整合可以帮助这些植物抵抗这种生态胁迫。这强烈的支持了这样一种观点，即克隆整合是根茎型克隆植物在长期的适应进化过程中形成的抵抗高强度沙埋的生态策略。 该区也生长着很多密集型克隆植物。养分的空间异质性在各种尺度上存在，密集型克隆植物也可能经历小尺度的养分异质性。以糙隐子草为研究对象，观察其在同质和异质养分条件下的生物量、生物量配置格局以及有性繁殖和克隆生长的权衡。结果表明：在异质性的养分条件下，相连的克隆片断的总体生物量、地上无性结构生物量、根生物量以及分株大小都显著高于切断的克隆片断;同样，异质性斑块中的相连的克隆片断的表现高于同质性斑块。这暗示着克隆整合能够帮助密集型克隆植物糙隐子草更好的利用小尺度的养分异质性。 此外，通过野外调查的方式观察该区两种重要的克隆半灌木，游击型的羊柴和密集型的油蒿在小尺度不同植被盖度斑块下的生物量配置格局。结果表明：羊柴的地上各部分生物量对植被盖度变化的响应不如油蒿敏感。这可能是因为羊柴的游击型克隆构型决定其可以跨越小尺度斑块实现克隆生理整合，从而利用不同小生境斑块的资源所致。油蒿只能利用小生境斑块内的资源，当小生境斑块的条件改变，其生物量以及配置方式也随之发生相应的变化。在繁殖方式上，羊柴的有性繁殖结构以及有性繁殖投资显著小于油蒿。在资源有限的条件下，对一种繁殖方式的投资常常会削弱另一种繁殖方式。羊柴主要依靠克隆生长，这符合并支持配置理论的观点。植物的空间格局与植物自身的生活史性状密切相关。羊柴和油蒿不同的生活史特性必然会在各自的种群空间格局中体现出来。本文还采用地统计学的方法，观察二者的种群空间格局。种群水平上，小尺度的空间自相关控制着羊柴种群的空间格局;油蒿种群的空间格局受更大尺度的过程控制，并在自身为建群种的群落随机分布。对于油蒿种群而言，发生在小于抽样尺度（<1m）的随机变异高于相应的羊柴种群。这两种克隆半灌木的种群空间格局的差异可能与二者克隆构型和克隆性的不同有关。 本文的研究对象不仅涉及根茎型克隆草本植物，还包括了克隆半灌木，不仅涉及游击型克隆植物，而且涵盖了密集型克隆植物。因此，本文的研究不仅有助于在理论上理解克隆植物对异质性生境的适应策略，在实践上也能为该区的生态恢复提供一定的理论依据。

Effects of grassland renovation on carbon concentrations and aggregate distribution in temperate grassland soils

The effects of continuous tillage on the distribution of soil organic matter (SOM) and aggregates have been well studied for arable soils. However, less is known about the effects of sporadic tillage on SOM and aggregate dynamics in grassland soils. The objectives of the present thesis were (I) to study the longer-term effects of sporadic tillage of grassland on organic carbon (Corg) stocks and the distribution of aggregates and SOM, (II) to investigate the combined effects of sporadic tillage and fertilization on carbon and nitrogen dynamics in grassland soils, and (III) to study the temporal dynamics of Corg stocks, aggregate distribution and microbial biomass in grassland soils. Soil samples were taken in three soil depths (0 – 10 cm; 10 – 25 cm; 25 – 40 cm) from a field trial with loamy sandy soils (Cambisols, Eutric Luvisols, Stagnosols, Anthrosols) north of Kiel, Germany. For Objective I we have sampled soil two and five years after one or two tillage operation(s). Treatments consisted of (i) permanent grassland, (ii) tillage of grassland followed by a re-establishment of grassland and (iii) tillage of grassland followed by a re-establishment of grassland with one season of winter wheat in between. The tillage in grassland led to a reduction in Corg stocks, large macroaggregates (>2000 µm) and SOM in the top 10 cm soil depth. These findings were still significant two years after tillage; however, five years after tillage no longer present. Regarding the soil profile (0 – 40 cm) no significant differences in the mentioned parameters between the tilled plots and the permanent grassland existed. A second tillage event and the insertion of one season of winter wheat did not lead to any further effects on Corg stocks as well as aggregate and SOM concentrations in comparison with a single tillage event in these grassland soils. Treatments adapted for Objective II included (i) long-term grassland and (ii) tillage of grassland followed by a re-establishment of grassland with one season of winter wheat in between. The plots were split and received either 240 kg N ha-1 year-1 in the form of cattle slurry or no cattle slurry application. The application of slurry within a period of four years had no effects on the Corg and total nitrogen stocks or the aggregate distribution, but led to a reduction of free and not physically protected SOM. However, the application of cattle slurry and the grassland renovation seems to change the plant species composition and therefore generalizations on the direct effects are not yet possible. For studying Objective III a further field trial was initiated in September 2010. Soil samples were taken six times within one year (from October 2010 to October 2011) (i) after the conversion from arable land into grassland, (ii) after the tillage of grassland followed by a re-establishment of grassland and (iii) in a permanent grassland. We found an increase in the microbial and fungal biomass after the conversion of arable land into grassland, but no effect on aggregate distribution and Corg stocks. A one-time tillage operation in grassland led to a reduction in large macroaggregates and Corg stocks in the top 10 cm soil depth with no effect on the sampled soil profile. However, we found large variations in the fungal biomass and aggregate distribution within one year in the permanent grassland, presumably caused by environmental factors. Overall, our results suggest that a single tillage operation in grassland soils markedly decreased the concentrations of Corg, larger aggregates and SOM. However, this does not result in long-lasting effects on the above mentioned parameters. The application of slurry cannot compensate the negative effects of a tillage event on aggregate concentrations or Corg stocks. However, while the Corg concentration is not subject to fluctuations within a year, there are large variations of the aggregate distribution even in a permanent grassland soil. Therefore conclusions of results from a single sampling time should be handled with care.

Determination of the gas diffusion coefficient of a peat grassland soil

Peatland habitats are important carbon stocks that also have the potential to be significant sources of greenhouse gases, particularly when subject to changes such as artificial drainage and application of fertilizer. Models aiming to estimate greenhouse gas release from peatlands require an accurate estimate of the diffusion coefficient of gas transport through soil (Ds). The availability of specific measurements for peatland soils is currently limited. This study measured Ds for a peat soil with an overlying clay horizon and compared values with those from widely available models. The Ds value of a sandy loam reference soil was measured for comparison. Using the Currie (1960) method, Ds was measured between an air-filled porosity (ϵ) range of 0 and 0.5 cm3 cm−3. Values of Ds for the peat cores ranged between 3.2 × 10−4 and 4.4 × 10−3 m2 hour−1, for loamy clay cores between 0 and 4.7 × 10−3 m2 hour−1 and for the sandy reference soil they were between 5.4 × 10−4 and 3.4 × 10−3 m2 hour−1. The agreement of measured and modelled values of relative diffusivity (Ds/D0, with D0 the diffusion coefficient through free air) varied with soil type; however, the Campbell (1985) model provided the best replication of measured values for all soils. This research therefore suggests that the use of the Campbell model in the absence of accurately measured Ds and porosity values for a study soil would be appropriate. Future research into methods to reduce shrinkage of peat during measurement and therefore allow measurement of Ds for a greater range of ϵ would be beneficial.

Change of composition and diversity of species and grassland management between different grazing intensity in Pannonian dry and wet grasslands

Investigations were carried out in wet and dry pasture. Coenological recordings were taken in three zones. The first zone (“A”) located 0-50 m near the stable, second zone (“B”) located 50-150 m from the stable, while the third zone (“C”) located farther than 150 m. We have carried out analyses of ecological and environmental factors and life form types. Based on our results for both dry and wet grasslands, quadrates of “A” zone were well isolated from the rest of the zones. Overgrazing, which involves considerable trampling, vanishes differences among vegetations, thereby promotes weed and disturbance tolerant rich vegetation. The lowest species number and diversity could be found here. Due to the nitrogen enrichment due to the constant presence of livestock, drier and less heat demanding habitat developed in the “A” zones, according to the environmental indicators. Because of the change in management, conservation and diversity values of “C” zone increased, however, according to nature protection values it underperformed compared to “B” zone. According to the sample area, wet grasslands from the sandy areas of Kiskunság, preserve nature protection values and grass composition better moving away from stables, due to less grazing pressure. Drier backgrounds tolerate stronger grazing pressure.

Zeolite from alkali modified kaolin increases NH4+ retention by sandy soil : column experiments

Sandy soils have low water and nutrient retention capabilities so that zeolite soil amendments are used for high value land uses including turf and horticulture to reduce leaching losses of NH4+ fertilisers. MesoLite is a zeolitic material made by caustic treatment of kaolin at 80-95oC. It has a moderately low surface area (9-12m2/g) and very high cation exchange capacity (494 cmol(+)/kg). Laboratory column experiments showed that an addition of 0.4% MesoLite to a sandy soil greatly (90%) reduced leaching of added NH4+ compared to an unamended soil and MesoLite is 11 times more efficient in retaining NH4+ than natural zeolite. Furthermore, NH4+-MesoLite slowly releases NH4+ to soil solution and is likely to be an effective slow release fertiliser.

Nitrogen pools and fluxes in grassland soils sequestering carbon

Carbon sequestration in agricultural, forest, and grassland soils has been promoted as a means by which substantial amounts of CO2 may be removed from the atmosphere, but few studies have evaluated the associated impacts on changes in soil N or net global warming potential (GWP). The purpose of this research was to ( 1) review the literature to examine how changes in grassland management that affect soil C also impact soil N, ( 2) assess the impact of different types of grassland management on changes in soil N and rates of change, and (3) evaluate changes in N2O fluxes from differently managed grassland ecosystems to assess net impacts on GWP. Soil C and N stocks either both increased or both decreased for most studies. Soil C and N sequestration were tightly linked, resulting in little change in C: N ratios with changes in management. Within grazing treatments N2O made a minor contribution to GWP (0.1-4%), but increases in N2O fluxes offset significant portions of C sequestration gains due to fertilization (10-125%) and conversion (average = 27%). Results from this work demonstrate that even when improved management practices result in considerable rates of C and N sequestration, changes in N2O fluxes can offset a substantial portion of gains by C sequestration. Even for cases in which C sequestration rates are not entirely offset by increases in N2O fluxes, small increases in N2O fluxes can substantially reduce C sequestration benefits. Conversely, reduction of N2O fluxes in grassland soils brought about by changes in management represents an opportunity to reduce the contribution of grasslands to net greenhouse gas forcing.

Grassland management activity data : current sources and future needs

Estimates of potential and actual C sequestration require areal information about various types of management activities. Forest surveys, land use data, and agricultural statistics contribute information enabling calculation of the impacts of current and historical land management on C sequestration in biomass (in forests) or in soil (in agricultural systems). Unfortunately little information exists on the distribution of various management activities that can impact soil C content in grassland systems. Limited information of this type restricts our ability to carry out bottom-up estimates of the current C balance of grasslands or to assess the potential for grasslands to act as C sinks with changes in management. Here we review currently available information about grassland management, how that information could be related to information about the impacts of management on soil C stocks, information that may be available in the future, and needs that remain to be filled before in-depth assessments may be carried out. We also evaluate constraints induced by variability in information sources within and between countries. It is readily apparent that activity data for grassland management is collected less frequently and on a coarser scale than data for forest or agricultural inventories and that grassland activity data cannot be directly translated into IPCC-type factors as is done for IPCC inventories of agricultural soils. However, those management data that are available can serve to delineate broad-scale differences in management activities within regions in which soil C is likely to change in response to changes in management. This, coupled with the distinct possibility of more intensive surveys planned in the future, may enable more accurate assessments of grassland C dynamics with higher resolution both spatially and in the number management activities.

Deriving grassland management factors for a carbon accounting method developed by the intergovernmental panel on climate change

Grassland management affects soil organic carbon (SOC) storage and can be used to mitigate greenhouse gas emissions. However, for a country to assess emission reductions due to grassland management, there must be an inventory method for estimating the change in SOC storage. The Intergovernmental Panel on Climate Change (IPCC) has developed a simple carbon accounting approach for this purpose, and here we derive new grassland management factors that represent the effect of changing management on carbon storage for this method. Our literature search identified 49 studies dealing with effects of management practices that either degraded or improved conditions relative to nominally managed grasslands. On average, degradation reduced SOC storage to 95% +/- 0.06 and 97% +/- 0.05 of carbon stored under nominal conditions in temperate and tropical regions, respectively. In contrast, improving grasslands with a single management activity enhanced SOC storage by 14% 0.06 and 17% +/- 0.05 in temperate and tropical regions, respectively, and with an additional improvement(s), storage increased by another 11% +/- 0.04. We applied the newly derived factor coefficients to analyze C sequestration potential for managed grasslands in the U.S., and found that over a 20-year period changing management could sequester from 5 to 142 Tg C yr(-1) or 0.1 to 0.9 Mg C ha(-1) yr(-1), depending on the level of change. This analysis provides revised factor coefficients for the IPCC method that can be used to estimate impacts of management; it also provides a methodological framework for countries to derive factor coefficients specific to conditions in their region.

Potential soil carbon sequestration in overgrazed grassland ecosystems

Excessive grazing pressure is detrimental to plant productivity and may lead to declines in soil organic matter. Soil organic matter is an important source of plant nutrients and can enhance soil aggregation, limit soil erosion, and can also increase cation exchange and water holding capacities, and is, therefore, a key regulator of grassland ecosystem processes. Changes in grassland management which reverse the process of declining productivity can potentially lead to increased soil C. Thus, rehabilitation of areas degraded by overgrazing can potentially sequester atmospheric C. We compiled data from the literature to evaluate the influence of grazing intensity on soil C. Based on data contained within these studies, we ascertained a positive linear relationship between potential C sequestration and mean annual precipitation which we extrapolated to estimate global C sequestration potential with rehabilitation of overgrazed grassland. The GLASOD and IGBP DISCover data sets were integrated to generate a map of overgrazed grassland area for each of four severity classes on each continent. Our regression model predicted losses of soil C with decreased grazing intensity in drier areas (precipitation less than 333 mm yr(-1)), but substantial sequestration in wetter areas. Most (93%) C sequestration potential occurred in areas with MAP less than 1800 mm. Universal rehabilitation of overgrazed grasslands can sequester approximately 45 Tg C yr(-1), most of which can be achieved simply by cessation of overgrazing and implementation of moderate grazing intensity. Institutional level investments by governments may be required to sequester additional C.