腾格里沙漠人工固沙植被演替生物土壤结皮盖度对沙埋的响应

生物土壤结皮(简称结皮)的形成与发展是沙区固沙植被建设成功的重要标志之一,其盖度随固沙植被演替的变化趋势是表征该植被系统地表稳定性的一个直观性生态学指标。利用空间代时间的方法,以腾格里沙漠不同始植年代(1956、1973、1981和1987年)固沙植被区发育的4种优势结皮-真藓(Bryum argenteum Hedw.)结皮、土生对齿藓(Didymodon vinealis(Brid.)Zand.)结皮、齿肋赤藓(Syntrichia caninervis Mitt.)结皮和藻-地衣-藓类混生结皮(Mixed crust)为研究对象,在测定结皮盖度、高度以及粗糙度随沙埋厚度逐渐增加变化的基础上,计算了使结皮盖度(从99.99%)开始降低的初始沙埋厚度(D1)和盖度降低为0%的临界沙埋厚度(D2),研究了该区固沙植被演替过程中结皮盖度对沙埋厚度增加的响应特征及其相关机制。结果显示:(1)4种结皮的盖度随沙埋厚度的增加呈logistic曲线逐渐降低。(2)在同一年代固沙区不同种间比较,混生结皮的D1值最小,D2值最大;真藓结皮的D1和D2值均小于其他两种藓类结皮;土生对齿藓结皮和齿肋赤藓结皮因固沙年限的不同而不同,在1956年固沙区,土生对齿藓结皮齿肋赤藓结皮,而在1973年固沙区和1981年固沙区,齿肋赤藓结皮土生对齿藓结皮。(3)随固沙植被演替,4种结皮盖度随沙埋厚度增加的降低速率逐渐减小,D1和D2值逐渐增大。(4)结皮总盖度随沙埋厚度增加的降低速率逐渐减小,表明随固沙植被演替,结皮对沙埋的抵御能力逐渐增强,固沙区植被系统地表稳定性增加。(5)结皮的粗糙度和高度随固沙植被演替逐渐增加,并显著影响了4种结皮盖度随沙埋厚度增加的降低速率、D1及D2值。研究为全面评估沙埋对沙区结皮结构、功能的影响乃至固沙植被稳定性提供了参考。     

腾格里沙漠人工固沙植被演替过程中生物土壤结皮归一化植被指数的变化特征

生物土壤结皮(简称结皮)影响干旱沙区生态系统归一化植被指数(NDVI)。该文基于空间代时间的方法,利用地物光谱仪采集腾格里沙漠不同始植年代(1956、1964和1973年)固沙植被区发育的5种优势结皮的NDVI数据,分析了固沙植被演替过程中结皮NDVI的变化特征及其对降水和温度变化的响应规律,并通过与固沙区主要地物进行比较,评估了结皮NDVI在该沙区生态系统NDVI中的作用。结果表明:1)随着固沙植被演替,结皮NDVI逐渐增加。不同种类结皮NDVI相比较,土生对齿藓(Didymodon vinealis)结皮真藓(Bryum argenteum)结皮混生结皮地衣结皮藻结皮。2)结皮NDVI受降水量、气温及二者间的交互作用影响显著,且具有明显的季节差异。结皮NDVI与降水量及其覆盖土壤浅层含水量均呈显著线性正相关关系,并且结皮NDVI对水分的敏感性随固沙植被演替而逐渐增加。结皮NDVI总体与日平均气温呈显著线性负相关关系,而与结皮表面温度呈显著指数负相关关系,并且结皮NDVI对温度的敏感性随固沙植被演替逐渐增加。结皮NDVI对温度变化的敏感性春季高于夏季,对水分变化的敏感性夏季高于春季。3)春季降水后,藓类结皮NDVI显著高于油蒿(Artemisia ordosica)、花棒(Hedysarum scoparium)、柠条(Caragana korshinskii)等灌木及裸沙;夏季降水后,结皮NDVI显著低于灌木。若考虑结皮较高的盖度,春、夏季结皮NDVI对固沙区系统NDVI的贡献率分别为90.01%和82.53%,均超过灌木(春季9.99%和夏季17.47%),并且结皮对固沙区系统NDVI的贡献率随着固沙植被演替而逐渐增加,而灌木的贡献率逐渐降低。该研究证明了在区域尺度上利用结皮NDVI并结合气象资料区分结皮演替阶段的可行性,并为干旱沙区在区域尺度上地表生态参量遥感估算的误差分析及结皮遥感监测的时相选择提供了数据基础。     

沙坡头植被固沙区生物结皮的发育特征

对沙坡头人工植被区内生物结皮的生物特征和非生物特征进行了调查，利用时空代换法研究了该地区生物结皮的发育和演替特征。结果表明：生物结皮层有着较快的成土过程，随固沙年限的增加，生物结皮的厚度以及结皮中粘土所占的比例增加，容重呈下降趋势；在各固沙年限的生物结皮覆盖区，构成生物结皮的主要优势生物成分为地衣、藻类和苔藓。不同发育年限和不同沙丘部位各类生物结皮的盖度的调查揭示，生物结皮的形成和发育有着重要的生物过程。对沙坡头植被固沙区生物结皮的演化过程进行了系统分析，发现生物结皮是在流沙固定过程中生物成分和非生物成分相互作用的产物，是降尘累积过程、生物过程和成土过程3个阶段的统一，并依据其发生学特点给出了3个发育阶段的定性划分。     

干旱半干旱地区人工固沙灌木林生态系统演变特征

应用实验生态学方法分析了沙坡头地区栽植于1956、1964、1981、1987年的无灌溉人工植被固沙群落浅层土壤分形特征、植被盖度、物种特征、生物量、土壤水分、土壤微生物,以及群落土壤物理和土壤养分特征,并与流动沙丘进行比较。结果表明,在干旱半干旱的草原化荒漠地区,首先利用半隐蔽式草方格沙障对流动沙丘进行固定,然后栽植灌木柠条、花棒等和半灌木油蒿,经过40多年的稳定演变,该区域逐渐形成由矮灌木与草本植物覆盖,以及隐花植物与微生物土壤结皮复合的固定沙丘景观。在人工植被固沙防护体系稳定演变过程中,浅表层土壤的细粒化和养分富集化特征,微生物土壤结皮与亚表层土壤厚度,以及浅表层土壤体积含水率均随固沙年限的延长趋于显著增加。而土壤微生物数量、植被盖度、植物种数等生物群落学属性在固沙年限达40a左右时,已趋于最大,尔后呈缓慢下降趋势。随着固沙年限的增加,灌木树种不断衰退减少,当固沙年限逾17a之后,群落生物量增至峰值后略有下降。土壤分形维数与土壤粘粒含量呈显著正相关关系,流动沙丘被人工植被固定年代越久远,浅表层(0~3cm)土壤粘粒含量(4.50%)越高,其分形维数越大(D=2.4083),表明人工植被固沙防护体系浅表层土壤结构变得越紧实,流动沙丘(D=2.0484)在人工植被的固定作用下,发生逆转的趋势越显著,沙丘日趋固定。     

固沙植物根际微生物对于沙土发育和流沙固定的影响

在宁夏中卫沙坡头铁路防沙研究地段,多年人工植被沙丘的沙土不断发育,在沙丘表面形成结皮层,结皮下面形成块状沙土层,导致沙丘逐渐固定,无疑这与机械沙障固沙和植物固沙措施有直接关系。从流动沙丘向固定沙丘不仅表面发生变化,内在因素的变化也起着重要作用,分别研究这些内外因素,探讨其相互     

雅鲁藏布江中游河谷风沙化土地砂生槐群落结构特征

基于样方调查和等级聚类分析,研究了雅鲁藏布江中游风沙化土地不同恢复演替阶段砂生槐群落的结构特征.结果表明:雅鲁藏布江中游风沙化土地植物群落可分为砂生槐群落、固沙草群落、砂生槐＜固沙草群落、砂生槐-固沙草群落、藏沙蒿+砂生槐群落和砂生槐+藏沙蒿群落6种类型.自然恢复演替从流动沙丘上分布的砂生槐对流沙的初步固定开始,随后固沙草开始侵入群落,逐渐形成了砂生槐-固沙草群落.另一种演替途径开始于固沙草群落,砂生槐在演替过程中出现在固沙草群落中,最后亦达到砂生槐-固沙草群落阶段.在一些半固定沙地阶段,藏沙蒿开始侵入群落,形成砂生槐+藏沙蒿群落.雅鲁藏布江风沙化土地的顶极群落是以砂生槐为优势种的灌丛群落.随着坡度增加,砂生槐群落盖度和高度有降低的趋势.生物结皮对土壤的理化性质有一定的改善作用,结皮覆盖处土壤水分含量显著高于其他演替阶段的表层土壤水分含量.流动沙地砂生槐灌丛冠幅、株高和萌蘖枝数量最高,其次是固定沙地,半固定沙地最低.各阶段枯死枝数量说明固定沙地阶段以后砂生槐种群有衰退的趋势.     

荒漠地衣对沙坡头人工植被固沙区的生态影响

腾格里沙漠东南缘沙坡头地区所形成的微型生物结皮(microbiotic crust)占优势的生态格局是荒漠地区天然植被中特有的生态景观之一。荒漠地衣作为微型生物结皮中重要的组成部分,在影响生态变化方面扮演着不可或缺的角色。本研究调查了不同建立年代的人工植被固沙区中的维管植物和微型生物结皮中地衣的物种组成和盖度,测定了结皮土壤的主要养分含量。结果显示:微型生物结皮中地衣以胶衣Collema和石果衣Endocarpon两属为优势类群;随人工植被建立时间的延长,维管植物和微型生物结皮盖度、结皮厚度与土壤养分含量呈增高趋势,并基本呈显著的正相关关系。维管植物、微型生物结皮、地衣和土壤养分基本一致的变化规律表明,微型生物结皮对固沙区中浅根系植被发育和土壤恢复具有正效应,为人工高效治沙及全面实施"沙漠生物地毯工程"提供了必要的理论基础。     

生物土壤结皮对荒漠土壤种子库和种子萌发的影响

研究了腾格里沙漠东南缘在不同自然条件（风、温度、水分）下,人工固沙植被区（24龄、41龄、50龄）和相邻天然植被区的两种生物土壤结皮对荒漠土壤种子库和种子萌发的影响。结果表明,荒漠土壤种子库在苔藓结皮上的储量显著高于藻类结皮。随着生物土壤结皮的发育,种子萌发量在苔藓结皮上增加,在藻类结皮上减少。生物土壤结皮层的含水量对种子萌发有显著的影响（p〈0.05）,植物种子在湿润处理的生物土壤结皮上的萌发量高于干燥处理的生物土壤结皮上的种子萌发量。生物土壤结皮表层温度和亚表层温度对荒漠植物种子萌发无显著影响（p〉0.05）,但总体而言,对于苔藓结皮,植物种子在较高温度下的萌发量略高于在较低温度下的萌发量,而对于藻类结皮,植物种子在较低温度下的萌发量略高。     

生物土壤结皮对荒漠土壤线虫群落的影响

在干旱的沙漠生态系统中,生物土壤结皮对于沙丘的固定和土壤生物的维持起着相当重要的作用.土壤线虫能敏感的指示土壤的恢复程度,是衡量沙区生态恢复与健康的重要生物学属性,而目前关于生物土壤结皮与土壤线虫的关系研究很少.为探明生物土壤结皮对土壤线虫的影响,以腾格里沙漠东南缘的人工植被固沙区藻结皮和藓类结皮覆盖的沙丘土壤为研究对象,根据固沙年限的不同将样地分为4个不同的区进行采样(1956、1964、1981和1991年固沙区),以流沙区作为对照;同时,在不同季度(4、7、9和12月)分别采集腾格里沙漠东南缘的人工植被固沙区藻结皮和藓类结皮覆盖下不同土层(0-10、10-20和20-30 cm)的沙丘土壤,以沙坡头地区的红卫天然植被区为对照,分析生物土壤结皮下土壤线虫的时空变化.采用改良的Baermann漏斗法进行分离线虫,用光学显微镜鉴定并统计.研究表明:1956、1964、1981和1991年人工植被固沙区的藻结皮和藓类结皮均可显著提高其下土壤线虫多度、属的丰富度、Shannon-Weaver多样性指数、富集指数和结构指数(P＜0.05),这可能是因为生物土壤结皮的存在为土壤线虫提供了重要的食物来源和适宜的生存环境;固沙年限与结皮下土壤线虫多度、属的丰富度、Shannon-Weaver多样性指数、富集指数和结构指数存在显著的正相关关系(P＜0.05),这说明固沙年限越久,越有利于土壤线虫的生存和繁衍;结皮类型显著影响土壤线虫群落,相对于藻结皮而言,藓类结皮下土壤线虫多度与属的丰富度更高(P＜0.05),这说明演替后期的藓类结皮比演替早期的藻结皮更有利于土壤线虫的生存和繁衍.此外,藻结皮和藓类结皮均可显著增加其下0-10、10-20和20-30 cm土层线虫多度和属的丰富度(P＜0.05),但随着土壤深度的增加,这种影响逐渐减弱,表明生物土壤结皮更有利于表层土壤线虫的生存;而且,随着季节的变化,藻结皮和藓类结皮下土壤线虫多度基本表现为秋季＞夏季＞春季＞冬季,这些反映了生物土壤结皮的生物量、盖度和种类组成随着季节变化而变化.因此,腾格里沙漠东南缘的人工植被固沙区生物土壤结皮的存在与演替有利于土壤线虫的生存和繁衍,增加了线虫数量、种类和多样性,这指示了生物土壤结皮有利于该区土壤及其相应生态系统的恢复.     

腾格里沙漠沙坡头地区荒漠地衣与生物地毯工程(英文)

文章论述了荒漠地衣与"沙漠生物地毯工程"。在沙坡头结皮微型生物中发现了23种地衣,其中两个新种已发表,一属6种为中国新记录。对于在腾格里沙漠东南角沙坡头地区人工植被固沙防护体系建成后的生态演替进行了分析。由于人工植被为形成结皮的微型生物提供了适宜的生长环境而导致微型生物结皮的形成和发育。在水分平衡规律的作用下漫长生态演替过程中,具有抽水机效应的人工植被使沙土深层水分消耗殆尽,从而导致人工植被自身逐年衰退。然而,与此相反的是无抽水机效应而具有固沙、固碳和抗旱功能的结皮微型生物却逐年形成并发育。这一结果为借助于结皮微型生物的接种技术在干旱沙漠构建"沙漠生物地毯工程"的可行性提供了科学依据。为了优化"沙漠生物地毯工程"利用荒漠地衣耐旱基因以构建转基因草地植物的研究也正在进行中。该研究是"沙漠生物地毯工程"基础研究的组成部分。     

半干旱沙地封育草场的植被变化及其与土壤因子间的关系

封育措施是一种主要的草场恢复和重建的措施。通过对半干旱沙地完全封育、季节封育和未封育地的比较分析,量化了不同封育措施下植被变化及其与土壤因子的关系。对3种封育措施群落组成和生物多样性的多响应置换过程(M RPP)分析结果表明,封育改变了群落的组成成分并增加了生物多样性,群落的指示种分析及样方相似性指数计算结果则显示,完全封育(>10a)的群落逐渐向旱生化发展,各植物种分布的空间异质性显著提高,放牧价值开始降低,而季节性封育则明显处于一种非平衡的稳定状态。对不同措施下植物种与土壤因子间关系除趋势对应分析(DCA)和除趋势典范对应分析(DCCA)排序结果表明,土壤水分状况是限制3种措施中植物种组成的决定性因子,生物结皮盖度、土壤有机质和土壤容重等因子均在一定的程度上对水分产生影响,其中最为突出的因子是生物结皮盖度,由于长期缺少牲畜的践踏,完全封育区内结皮发育较好,这也是导致群落向旱生化发展的原因之一,同时一些重要因子诸如降水的时空变化或由此而引发的土壤水分的时空变化在本研究中可能被忽略。相关分析表明3种措施的生物多样性除了受土壤水分状况(土壤含水量和结皮盖度)的影响外,还与土壤速效氮呈正相关,与速效磷呈负相关。     

Effect of microbiotic soil surface crusts on emergence of vascular plants

Microbiotic crusts are a common and widespread feature of arid and semi-arid landscapes. Their effect on vascular plant success has been discussed controversially. However, only very few field studies have yet tried to experimentally investigate the effect of microbiotic crusts on vascular plant establishment.In this study we investigate the influence of cyanobacteria dominated microbiotic soil surface crust on vascular plants in a desert sand dune area by using a series of manipulative experiments. Crusts were disturbed and removed and density response to these treatments was monitored during the two following years.Emergence densities of vascular plants were considerably higher when crusts were removed and destroyed. This effect was particularly pronounced when the disturbances were applied before the main seed dispersal period. By experimentally preventing seed dispersal into disturbed areas we could show that undisturbed crusts reduce the probability for seeds to come to rest. This indicates that soil surface roughness is a major determinant for the establishment of vascular plants in the study area. We conclude that small-scale and well-timed disturbances of microbiotic crusts in arid lands may increase vascular plant establishment probabilities. A potential feedback process of long-term vegetation dynamics is suggested: disturbance of microbiotic crusts results in higher numbers of emerging plants, which in turn represent a rough seed-trapping element leading to a further increase in densities in consecutive years.     

Exclusion effects on vegetation characteristics and their correlation to soil factors in the semi-arid rangeland of Mu Us Sandland,China

Exclusion has been applied as a main measure for re-vegetation all over the world.This paper,by comparing the results of year-round exclusion,seasonal exclusion,and non-exclusion,quantified the vegetation variations under three different exclusion measures and their correlation to soil factors.The analysis results for community species component and plant diversity using multi-response permutation procedures (MRPPs)showed that exclusion did change the species component and increase plant diversity remarkably,while the period of exclusion had no significant influence on these two community features.The indicator species analysis and calculation of similarity indices indicated that community for year-round exclusion were becoming xerophytization and unpalatability,and showed highly spatial heterogeneity of plant species distribution,whereas community for seasonal exclusion was under stable non-equilibrium condition.Detrended correspondence analysis (DCA)and detrend canonical correspondence analysis (DCCA)results of relationship between plant species and soil variables demonstrated that soil moisture was a controlling factor for plant species component,microbiotic soil crust cover,soil organic matter,and soil bulk density had significant effects on soil moisture,among which microbiotic soil crust was a leading factor owing to its limitation to rainfall infiltration on the one hand,and its constraints to entrance of herbaceous seeds into soil or to germination of soil seeds on the other hand.As a result of long-term removal of animal grazing,crust kept intact in year-round exclusion community,which was a main reason of community xerophytization.It was also obvious from ordination results that some important environmental factors,such as tempo-spatial change of rainfall and corresponding tempo-spatial change of soil moisture,were neglected during direct gradient analysis.In addition,biodiversity was close related to soil nutrients as well as to soil moisture condition (soil water content and crust cover),and it had positive relation to available N,and negative relation to available P.Higher soil N had advantage to non-leguminous plants growth on nutrition-poor sand land definitely.The impact of P to community component was unclear and should be studied from plant physiology.Further researches on nonequilibrium theory in semi-arid rangeland will provide a scientific and flexible animal development paradigm for being implementing livestock fen-raising and grazing-forbidden policies in China.     

Characteristics of normalized difference vegetation index of biological soil crust during the succession process of artificial sand-fixing vegetation in the Tengger Desert,Northern China

Aims Biological soil crust (hereafter crust) affects normalized difference vegetation index (NDVI) values in arid desert ecosystems. This study aimed to demonstrate the feasibility of combining crust NDVI values with meteorological data to distinguish the crust successional stage at the regional scale. Meanwhile, the characteristics of crust NDVI could provide the basis for the error analysis of NDVI-based surface ecological parameters estimation in desert ecosystems. We also suggested the optimum periods for crust observation based on the multi-temporal remote sensing images.Methods NDVI values of five types of dominant crusts, three typical sand-fixing shrubs and bare sand were collected by spectrometer in the field. Crusts and shrubs were randomly selected in revegetated areas established in 1956, 1964, and 1973 at Shapotou, which is on the southeastern edge of the Tengger Desert. We used the space-for-time method to study the characteristics of crust NDVI values and their responses to precipitation and temperature during the succession process of artificial sand-fixing vegetation. Additionally, we evaluated the contribution of crust NDVI values to the whole ecosystem NDVI values by comparing the NDVI values of crusts, shrubs and bare sand.Important findings 1) With succession process of the artificial sand-fixing vegetation, the crust NDVI values significantly increased. Among different crust types, we found the following order of NDVI values: Didymodon vinealis crust > Bryum argenteum crust > mixed crust > lichen crust > algae crust. 2) Crust NDVI values were significantly affected by precipitation, temperature and their interaction, and the influences showed significant seasonal differences. Furthermore, we found significantly linear correlations between crust NDVI value and precipitation, and between crust NDVI value and the shallow soil moisture content covered by crust. A significantly negative linear correlation between daily mean temperature and crust NDVI value, and a significantly exponential correlation between the surface temperature of crust and its NDVI value. With the succession process of artificial sand-fixing vegetation, the response of crust NDVI value to precipitation and temperature became more sensitive. In addition, the response of crust NDVI value to temperature was more sensitive in spring than in summer, while that to precipitation was less sensitive in spring than in summer. 3) Moss crust NDVI value was significantly higher than that of shrubs and bare sand after the rainfall event in spring, while shrubs NDVI value was significantly higher than that of crust after the rainfall event in summer. Considering the coverage weights of different ground features in sand-fixing areas, crust NDVI values contributed 90.01% and 82.53% in spring and summer, respectively, to the regional NDVI values, which were higher than those of shrubs (9.99% and 17.47% in spring and in summer, respectively). Additionally, with the succession process of artificial sand-fixing vegetation, crust NDVI values contributed more, while shrubs contributed less to regional NDVI values.     

荒漠地衣结皮研究进展

微型生物结皮在干旱、半干旱荒漠地区广泛分布,对维持荒漠生态系统的稳定性具有重要作用。地衣结皮是微型生物结皮的重要组成部分及主要类型之一,在固沙、固碳和固氮能力方面独具优势。本文从区域尺度和局部尺度综述了国内外荒漠地衣分布、群落组成及其影响因素,从微尺度探讨了荒漠地衣在形成过程中可能相关的生物因子的作用与功能。虽已有研究发现气候类型、降水量、土壤理化性质、微地形和温度会对荒漠地衣生长型、种类、丰度及盖度产生影响,来自地衣体、地衣结皮和地衣结皮土壤中的生物因素与维持地衣正常生命活动及分布之间存在相关关系,但上述结论尚具有一定的局限性,主要表现在区域尺度仍缺乏专门对荒漠地衣的研究,微尺度缺乏对地衣相关生物功能的实验性探索及验证。上述局限在一定程度上限制了通过人工手段大规模应用荒漠地衣结皮的研究。本文基于国内外研究进展及存在问题,对荒漠地衣结皮应用进行了展望,以期为人工构建荒漠地衣结皮和干旱、半干旱荒漠治理及生态恢复提供新的思路和参考。     

Exclusion effects on vegetation characteristics and their correlation to soil factors in the semi-arid rangeland of Mu Us Sandland, China

Exclusion has been applied as a main measure for re-vegetation all over the world. This paper, by comparing the results of year-round exclusion, seasonal exclusion, and non-exclusion, quantified the vegetation variations under three different exclusion measures and their correlation to soil factors. The analysis results for community species component and plant diversity using multi-response permutation procedures (MRPPs) showed that exclusion did change the species component and increase plant diversity remarkably, while the period of exclusion had no significant influence on these two community features. The indicator species analysis and calculation of similarity indices indicated that community for year-round exclusion were becoming xerophytization and unpalatability, and showed highly spatial heterogeneity of plant species distribution, whereas community for seasonal exclusion was under stable non-equilibrium condition. Detrended correspondence analysis (DCA) and detrend canonical correspondence analysis (DCCA) results of relationship between plant species and soil variables demonstrated that soil moisture was a controlling factor for plant species component, microbiotic soil crust cover, soil organic matter, and soil bulk density had significant effects on soil moisture, among which microbiotic soil crust was a leading factor owing to its limitation to rainfall infiltration on the one hand, and its constraints to entrance of herbaceous seeds into soil or to germination of soil seeds on the other hand. As a result of long-term removal of animal grazing, crust kept intact in year-round exclusion community, which was a main reason of community xerophytization. It was also obvious from ordination results that some important environmental factors, such as tempo-spatial change of rainfall and corresponding tempo-spatial change of soil moisture, were neglected during direct gradient analysis. In addition, biodiversity was close related to soil nutrients as well as to soil moisture condition (soil water content and crust cover), and it had positive relation to available N, and negative relation to available P. Higher soil N had advantage to non-leguminous plants growth on nutrition-poor sand land definitely. The impact of P to community component was unclear and should be studied from plant physiology. Further researches on non-equilibrium theory in semi-arid rangeland will provide a scientific and flexible animal development paradigm for being implementing livestock fen-raising and grazing-forbidden policies in China. __________ Translated from Acta Ecologica Sinica, 2005, 25(12): 3212–3219 [译自: 生态学报]     

荒漠地表生物土壤结皮形成与演替特征概述

土壤表面结皮是世界范围内干旱沙漠地区土壤表面广泛存在的自然现象,包括物理结皮和生物土壤结皮两大类型。其中,生物土壤结皮作为干旱沙漠地区特殊环境的产物,是由细菌、真菌、蓝绿藻、地衣和苔藓植物与土壤形成的有机复合体。它的形成使土壤表面在物理、化学和生物学特性上均明显不同于松散沙土,具有较强的抗风蚀功能和重要的生态效应,成为干旱沙漠地区植被演替的重要基础。随着形成生物土壤结皮的物种更替,维持结皮结构的主要胶结方式亦随之发生变化,即由胞外多糖的粘结作用逐渐转变为蓝藻和荒漠藻的藻丝体、地衣菌丝体以及苔藓植物假根的缠绕和捆绑作用,物种更替是结皮微结构和胶结方式转化的生物基础。生物土壤结皮的形成通常可以分为以下几个阶段:生物土壤结皮的早期阶段(土壤酶和土壤微生物),藻结皮阶段、地衣结皮阶段和苔藓结皮阶段。即随着土壤微生物在沙土表面的生长,随后出现丝状蓝藻和荒漠藻类植物,形成以藻类植物为主体的荒漠藻结皮;当土壤表面得到一定固定后,便开始出现地衣和苔藓植物,形成以地衣和苔藓植物为优势的生物结皮类型。其中,前一阶段的完成又为后一阶段的开始提供良好的环境条件。当环境条件适宜时,生物土壤结皮也可以不经历其中某个阶段而直接发育到更高级的阶段。     

Evolutionary characteristics of the artificially revegetated shrub ecosystem in the Tengger Desert, northern China

The rain-fed sand-binding vegetation which stabilizes the migrating desert dunes in the Shapotou area at the southeastern edge of the Tengger Desert was initiated in 1956. The shrubs initially employed were predominantly Caragana korshinskii, Hedysarum scoparium, and Artemisia ordosica, and a desert shrub ecosystem with a dwarf shrub and microbiotic soil crust cover on the stabilized sand dunes has since developed. Since 1956 the success of this effort has not only ensured the smooth operation of the Baotou–Lanzhou railway in the sand dune area but has also played an important role in the restoration of the local eco-environment; therefore, it is viewed as a successful model for desertification control and ecological restoration along the transport infrastructure in the arid desert region of China. Some of the effects of recovery from desertification and ecological restoration on soil properties are shown by the increase in the distribution of fine soil particles, organic matter, and nutrients. The physical surface structure of the stabilized sand dunes, and inorganic soil crusts formed by atmospheric dust, have also led to the gradual formation of microbiotic soil crusts. Sand dune stabilization is associated with: (1) decreased soil particle size, (2) increased total N, (3) increased thickness of microbiotic crusts, (4) increased thickness of subsoil, and (5) an increase in volumetric soil moisture in the near-surface environment. After 17 years of dune stabilization, both the number of shrubs and community biomass decreased. The number of microbes, plant species and vegetation cover, all attained a maximum after the dunes had stabilized for 40 years. There is a significant positive correlation between the fractal dimension of soil particle size distribution (PSD) and the clay content of the shallow soil profile in the desert shrub ecosystem; the longer the period of dune stabilization, the greater the soil clay content in the shallow soil profiles (0–3 cm), and the greater the fractal dimension of soil PSD. This reflects the fact that during the revegetation processes, the soil structure is better developed, especially in the upper profile. Hence, the migrating sand dune becomes more stabilized. Therefore, the fractal model can be used to describe the texture and fertility of the soil, and, along with the degree of stability of the previously migrating sand dunes, can be used as an integrated quantitative index to evaluate the revegetation practice in the sand dune areas and their stabilization.     

Long-Term Ecosystem Effects of Sand-Binding Vegetation in the Tengger Desert, Northern China

The planting of sand‐binding vegetation in the Shapotou region at the southeastern edge of the Tengger Desert began in 1956. Over the past 46 years, it has not only insured the smooth operation of the Baotou–Lanzhou railway in the sand dune section but has also played an important role in the restoration of the local eco‐environment; therefore, it is viewed as a successful model for desertification control and ecological restoration along the transport line in the arid desert region of China. Long‐term monitoring and focused research show that within 4–5 years of establishment of sand‐binding vegetation, the physical surface structure of the sand dunes stabilized, and inorganic soil crusts formed by atmospheric dust gradually turned into microbiotic crusts. Among the organisms comprising these crusts are cryptogams such as desert algae and mosses. In the 46 years since establishing sand‐binding vegetation, some 24 algal species occurred in the crusts. However, only five moss species were identified, which was fewer than the species number in the crust of naturally fixed sand dunes. Other results of the planting were that near‐surface wind velocity in the 46‐year‐old vegetation area was reduced by 54.2% compared with that in the moving sand area; soil organic matter increased from 0.06% in moving sand dunes to 1.34% in the 46‐year‐old vegetation area; the main nutrients N, P, K, etc., in the desert ecosystem increased; soil physicochemical properties improved; and soil‐forming processes occurred in the dune surface layer. Overall, establishment of sand‐binding vegetation significantly impacted soil water cycles, creating favorable conditions for colonization by many herbaceous species. These herbaceous species, in turn, facilitated the colonization and persistence of birds, insects, soil animals, and desert animals. Forty‐six years later, some 28 bird species and 50 insect species were identified in the vegetated dune field. Thus, establishment of a relatively simple community of sand‐binding species led to the transformation of the relatively barren dune environment into a desert ecosystem with complex structure, composition, and function. This restoration effort shows the potential for short‐term manipulation of environmental variables (i.e., plant cover via artificial vegetation establishment) to begin the long‐term process of ecological restoration, particularly in arid climates, and demonstrates several techniques that can be used to scientifically monitor progress in large‐scale restoration projects.