我国南方4种常见人工林林下植物多样性特征及影响因素

为了解长期植被恢复的成熟人工林林下植物组成与多样性特征及其影响因素,基于广东鹤山生态系统国家野外科学观测研究站的南亚热带人工林生态系统,对环境相似(坡度、坡向、海拔)、30 a生4种类型人工林(桉树混交林、马占相思纯林、乡土混交林、针叶混交林)进行调查研究,分析林下植物组成和物种多样性(Shannon-Wiener指数、Simpson指数、Pielou指数)特征。结果表明,人工林林下植物类型丰富,均可形成乔-灌-草垂直结构;4种林型林下植物组成既有相似性,也有差异性,桉树混交林与针叶混交林、马占相思纯林与乡土混交林的灌木层组成相似;桉树混交林与马占相思纯林、乡土混交林与针叶混交林的草本层组成相似,而桉树混交林与针叶混交林的草本层组成极不相似。林分类型影响林下植物多样性,马占相思纯林林下灌草多样性显著低于其他3种混交林(P<0.05),灌木物种数、个体数最少;针叶混交林林下物种丰富度最高。林分郁闭度与林下植物多样性呈正相关(P<0.001),林下植物分布与土壤养分含量相关,桉树混交林、马占相思纯林林下植物多样性与不同形态氮含量相关,有效磷、全磷影响乡土混交林林下物种的分布,针叶混交林受土壤酸碱度、全钾的影响较为明显。在4种人工林林下植物群落中,乡土混交林多样性,均匀度最高,优势度最低,具有更佳的保育和维持林下生物多样性功能。因此,乡土树种混交林更适用于生态公益林构建或对一些针叶林及外来树种纯林进行林分改造。     

外来树种华北落叶松引种对秦岭森林群落的影响

采用样地调查法对比研究了秦岭火地塘林区外来树种华北落叶松人工林与乡土树种华山松人工林及华山松天然次生林群落特征差异.结果表明:华北落叶松人工林群落与华山松天然次生林群落的相似性系数仅为0.11,华山松天然次生林与华山松人工林的物种数量均明显高于华北落叶松人工林(P＜0.01);华山松天然次生林和华山松人工林乔、灌、草层的Margalef指数、Simpson指数、Shannon-Wiener指数和Pielou均匀度指数均显著高于华北落叶松人工林( P＜0.001),而前两者之间灌木层和草本层的4个多样性指数的差异不显著(P＞0.05);华北落叶松人工林的自然构成系数最低(0.3),华山松天然次生林的自然构成系数最高(5.2),华山松人工林的自然构成系数为3.5,三者存在极显著差异(P＜0.001).说明外来树种华北落叶松引种造成秦岭森林群落物种丰富度、植物多样性和林分自然化程度降低,自然次生演替或乡土树种人工林较外来树种人工林更有利于林下植被的恢复.     

引种桉树对本地生物多样性的影响

桉树以速生和适应多种环境的特性成为世界著名的造林树种.但引种桉树对环境可能产生负面影响,如导致土地退化、地下水水位下降和多样性降低等,特别是对林下本地生物物种多样性的影响及其原因还存有争议.本文对此进行了综述,认为大部分桉树人工林本地物种数量低于天然林,一般不高于乡土树种人工林,但总体上好于其他外来树种人工林.导致桉树人工林生物多样性低的原因主要是桉树的生理生态特性、人类不合理的规划和砍伐等,其中人为因素起主导作用.若根据引种地的群落性质,通过严格的设计和科学管理,可以将这种负面影响最小化.应按照有利于群落正常发育和植被更新的方式栽种桉树人工林,保留天然植被,减少人为干扰,从而减轻引种桉树的负面影响.     

黄土高原子午岭油松林的种子雨和土壤种子库动态

对黄土高原区子午岭不同林龄(18a、29a、40a、54a)油松(Pinus tabulaeformis carr.)人工林及天然林(约75a)的种子雨和土壤种子库进行了研究.结果表明,该区油松种子雨一般从每年9月初开始,一直到11月底结束,种子雨降落历程与林龄大小有关,种子雨发生时间和降落高峰期有所不同.不同林龄的油松种子雨强度不同,种子雨总量大小顺序为:40a人工林((489 9±8.64)粒· m-2)＞29a人工林((346.8±7.45)粒· m-2)＞54a人工林((327.1±8.13)粒· m-2)＞天然林((146.9±5.25)粒· m-2)＞18a人工林((78.1±2.72)粒· m-2).种子雨总量随林龄的增加而增加,约40a时达到高峰,种子雨活力也以40a时最高.不同林龄油松林土壤种子库存在显著差异,其中18a人工林种子库最小,40a人工林种子库最大.从种子雨降落到次年4月,5种林分土壤种子库总量下降了42.34%～53.59%,空粒种子增加了26.72%～48.69%;从4月到8月份种子腐烂率由10.28%～13 62%增加到57.25%～63.28%.动物的搬运、取食和种子腐烂死亡是种子库损耗的主要因素.土壤种子库中的油松种子主要集中在枯枝落叶层,其次为0～2cm层,2～10cm层种子最少.到8月中旬,土壤中98.26%的油松种子都已丧失活性.不同林分下油松幼苗的密度差异较大,40a人工林下幼苗最多,其余依次为29a人工林、54a人工林和天然林,18a人工林下的实生苗极少,幼苗死亡率极高.在一定龄级范围内,人工林结实能力和更新潜力随林龄增加而增加,40a时更新潜力最大.虽然有大量种子下落,但由于种子大量损耗和幼苗死亡,通过环境筛作用而最终可以成熟的个体数量十分有限.     

不同起源格氏栲林分下土壤微生物生态分布的初步研究

本文研究了福建三明小湖天然起源和人工起源的格氏栲林下土壤微生物的生态分布。两种起源的格氏栲林下土壤微生物中细菌占绝对优势,人工林芽孢杆菌所占细菌总数比例远大于天然林;天然林微生物总数、细菌、真菌以及固氮菌等生理类群的数量均高于人工林,而且,随着坡位的下降表现为由低至高的递增趋势。青霉和木霉是土壤真菌的优势种属,链霉菌属中的白色类群和黄色类群构成了土壤放线菌的主要组分,但在天然林中的数量明显低于人工林。     

外来树种日本落叶松和日本花柏对鄂西北森林群落的影响

【目的】研究大面积栽植外来树种日本落叶松和日本花柏对鄂西北森林群落物种多样性的影响,为评价外来树种的入侵风险提供依据。【方法】采用样地调查法对比研究外来树种日本落叶松和日本花柏人工林与当地森林群落特征差异。【结果】日本落叶松人工林样地林下植物种类丰富,样地平均物种数与当地天然林样地物种数相比无显著差异;林下灌木层和草本层多样性指数较高,草本层多样性指数与当地天然林相比无显著差异;林下未发现日本落叶松的更新苗。日本花柏人工林样地平均物种数显著少于当地其他人工林样地;乔木层、灌木层和草本层的4个多样性指数值均小于当地其他人工林样地;在3个样地中出现日本花柏更新苗,更新苗数量达479株·hm~(-2)。【结论】引种栽培日本落叶松不会导致当地森林群落的物种多样性降低,不会引起生物入侵风险;但引种栽培日本花柏会明显降低当地森林群落的物种多样性,对当地森林生态系统的稳定构成一定威胁。     

毛红椿天然林种子雨、种子库与天然更新

2008-2011年,调查江西九连山国家级自然保护区毛红椿天然林的种子雨、种子库及林下幼苗数量.结果表明:在毛红椿天然林,种子雨散布时间为10月下旬至12月下旬.2010年不同样地的种子雨强度为虾公塘气象观测站(320.3±23.5粒·m-2)＞虾公塘保护站(284.7±24.2粒·m-2)＞大丘田保护站(251.6±24.7粒·m-2),分别以222.0、34.3和22.6粒·m-2完好种子供土壤萌发更新;毛红椿种子储量取决于结实量、鸟类取食和种子活力等因素,鸟类取食是其种子储量大幅下降的首要因素;由于种子不耐储藏以及大量腐烂,种子有效贮藏期不足1个月.12月天然林种子库平均萌发数≤2株·m-2,次年1月土壤种子库种子量最少,为6.7～11.8粒·m-2,平均仅萌发0.4～0.6株·m-2,与林下实生幼苗分布极少相吻合.毛红椿种子雨储备、种子库种子活力保存及幼苗建成等因素影响其天然更新.     

固氮树种旱冬瓜对退化林地土壤修复和林下植被重建的生态驱动效应

固氮树种对退化土壤和森林的结构与功能修复和改良具有重要价值,但是,固氮树种的混交配置、林龄变化和人工与天然起源林分对土壤修复和林下植被重建方面的生态驱动效应与影响机制的认识尚不够深入。因此,在金沙江上游选择退耕地上不同混交配置模式、不同林龄旱冬瓜(Alnus nepalensis)人工林和旱冬瓜天然次生林,对比分析了土壤养分、林下植被生长、林下植被多样性和旱冬瓜材积等指标的差异,以期阐明固氮树种旱冬瓜对土壤养分状况及林下植被重建的生态驱动效应。结果表明：(1)不同旱冬瓜人工林配置模式中,旱冬瓜纯林的土壤养分综合指标显著高于旱冬瓜+云南松混交林和云南松纯林(P<0.05);(2)不同林龄旱冬瓜人工林中土壤有机质、总氮及土壤养分综合指标呈现8年生林均显著大于5年生林(P<0.05);(3)土壤有机质、总氮及土壤养分综合指标均为旱冬瓜天然林>旱冬瓜和云南松人工混交林>云南松天然林(P<0.05);(4)SEM模型分析发现,旱冬瓜材积与土壤养分综合指标呈极显著的正相关关系(R=0.473,P<0.001);(5)在不同旱冬瓜人工配置模式和不同优势种的天然林中...     

南亚热带乡土树种与桉树人工林土壤真菌群落多样性和功能类群的比较

营造乡土树种人工林和桉树人工林是我国南亚热带森林经营的常见模式。为探究土壤真菌群落多样性及功能对乡土树种和桉树人工林的响应特征与机制,该研究以南亚热带4个乡土树种人工林[马尾松(Pinus massoniana)、火力楠(Michelia macclurei)、米老排(Mytilaria laosensis)、红锥(Castanopsis hystrix)]和外来树种尾巨桉(Eucalyptus urophylla × E. grandis)人工林为对象,基于各林分土壤(0～20 cm)真菌18S rRNA高通量测序数据,利用FUNGuild数据库,比较分析乡土树种与尾巨桉人工林土壤真菌群落多样性和功能类群的差异特性及影响的主导土壤环境因子。结果表明:(1)5个研究林分的土壤真菌优势门均为子囊菌门和担子菌门,但不同乡土树种林分与尾巨桉林的土壤真菌优势目存在差异。(2)尾巨桉林土壤真菌群落α多样性高于乡土树种人工林,其群落组成结构也与乡土树种人工林存在显著差异(P<0.05)。(3)4个乡土树种人工林土壤的腐生营养型的相对丰度高于尾巨桉林,并且火力楠林和米老排林土壤丛枝菌根真菌的相对丰度明显高于尾巨桉林,尾巨桉林土壤共生营养型以及外生菌根真菌和木材腐生菌的相对丰度明显高于乡土树种人工林。(4)pH是导致尾巨桉林与乡土树种人工林土壤真菌群落多样性和功能类群差异的主要土壤环境因子。综上认为,在南亚热带地区将尾巨桉林改建成火力楠林或米老排林可提高土壤养分水平,提升土壤生态功能。     

树种及多样性组配对南亚热带人工林早期树木生长的影响

为科学筛选提升南亚热带人工林生产力的树种配置模式,选择南亚热带8个乡土树种,采用随机区组的试验设计,建立了树种多样性梯度(1、2、4、6个树种)人工新造林试验平台,研究树种多样性及不同功能特性树种混交对人工林早期树木生长的影响。结果表明: 在树木生长第5年,树木生长并没有随树种多样性增加而增加;速生树种马尾松和米老排纯林生长量是珍贵树种红椎和格木纯林的2.5～4.5倍;2个树种混交和4个树种混交情况下,针阔树种混交、速生树种与固氮树种混交显著提高树木生长量51.5%～132.8%,而当6个树种混交时,不同树种组配对生长量没有显著影响。不同树种配置模式下土壤氮、磷养分是影响树木早期生长的主要因素。针阔树种混交、速生和固氮树种混交能显著提高南亚热带人工林树木的早期生长。     

The potential of small Eucalyptus plantations in farmscapes to foster native woody plant diversity: local and landscape constraints

The major focus of ecological restorations has been on understanding local factors. However, landscape factors such as dispersal limitation of individuals or propagules across the surrounding matrix can also constrain the restoration progress. We investigated to what extent native woody species colonize and thrive in plantations, focusing on both the role of local factors such as grazing and canopy cover as well as on landscape factors. We recorded all native tree and shrub species in 60 small Eucalyptus plantations embedded in an open agricultural landscape at 0.1–12 km from a remnant continuous forest in central Ethiopia. We found a total of 1,571 individuals of native woody plants belonging to 55 species. Number of such species in a plantation increased significantly with the height of the grass sword indicating their sensitivity to grazing. Moreover, the number of woody species in the patches decreased significantly with distance to the forest. Our results illustrate the need for regulating the grazing pressure for a successful regeneration of native species in Eucalyptus plantations. In addition, sowing or planting native trees will be necessary in most plantations, as only few remnant natural forests that could act as seed sources occur across the Ethiopian highlands. Another main obstacle might be the prohibition of selling timber of native trees, which indirectly discourage farmers from letting native trees regenerate. Thus, the increasing cover of Eucalyptus seen across the country will not automatically foster a recovery of native woody plant biodiversity, even if managed to optimize local environmental conditions.     

Restoration of semi-natural forest after clearcutting of conifer plantations in Japan

We reviewed recent studies on the restoration of semi-natural forests after clearcutting of conifer plantations with specific reference to the importance of setting restoration goals, general and specific factors influencing restoration, and the prediction and judgment of successful restoration. For the restoration of semi-natural forests following the clearcutting of conifer plantations, recovery levels and appropriate restoration methods cannot be considered separately from the aims of restoration to provide ecosystem services. Restoration needs to be based on the setting of goals that correspond to the type and degree of ecosystem services targeted. When we aim to restore vegetation dominated by late-seral canopy trees within as short a period after the clearcutting of conifer plantations as possible, advanced regeneration in the pre-logged plantation is the most important and reliable source of post-logging regeneration, just as it is in the recovery of disturbed non-plantation forests. Advanced regeneration is not always present in plantations. Seedling establishment by seed rain from adjacent natural forest patches after a disturbance can contribute to late-seral or canopy species; however, the range of the edge effect is generally short, and the degree of the edge effect depends on the natural forest type and is more pronounced in deciduous forests, such as those in cool-temperate climates, or in forests with a complex forest structure. Thus, advanced regeneration is a better predictor of short-term forest recovery than measures based on seed rain from adjacent seed sources. However, restoration achieved only through advanced regeneration can simplify the species composition, and the recolonization processes of gradual species accession from seeds should be considered in the long-term context of restoration.     

Establishment of tree seedlings in the understory of restoration plantations: natural regeneration and enrichment plantings

Little is known about the potential of restoration plantations to provide appropriate understory conditions to support the establishment of seeds arriving from neighboring native forests. In this article, we investigated how seedling establishment is affected in the understory of restoration sites of different ages and assessed some of the potential environmental factors controlling this ecological process. We first compared the density and richness of native tree seedlings among 10‐, 22‐, and 55‐year‐old restoration plantations within the Atlantic Forest region of southeastern Brazil. Then, we undertook a seed addition experiment in each study site, during the wet season, and compared seedling emergence, survival, and biomass on local versus old‐growth forest soil (transferred from a reference ecosystem), in order to test whether local substrate could hamper seedling establishment. As expected, the oldest restoration site had higher density and richness of spontaneously regenerating seedlings. However, seedling establishment was less successful both in the oldest restoration planting and using substrate transferred from a reference ecosystem, where emergence and survival were lower, but surviving seedlings grew better. We attribute these results to lower light availability for seedlings in the understory of the oldest site and speculate that higher incidence of pathogens on old‐growth forest soil may have increased seedling mortality. We conclude that the understory of young restoration plantations provides suitable microsite conditions at the early establishment phases for the spontaneous regeneration or enrichment planting of native trees.     

Contrasting Cloud Forest Restoration Potential Between Plantations of Different Exotic Tree Species

The role of exotic tree plantations for biodiversity conservation is contested. Such plantations nevertheless offer various ecosystem service benefits, which include carbon storage and facilitation of indigenous tree species regeneration. To assess forest restoration potential in tropical exotic tree plantations, we assessed native cloud forest tree regeneration in 166 plots in ca. 50‐year‐old plantations of five timber species that are widely used in tropical plantations (Pinus patula, Eucalyptus saligna, Cupressus lusitanica, Grevillea robusta and Acacia mearnsii). Differences in species abundance, diversity and composition were compared among plantations, and between plantations and disturbed and undisturbed indigenous Afromontane cloud forest (southeast Kenya) relicts after controlling for environmental variation between plots (i.e. altitude, distance to indigenous forest, soil depth, slope, aspect) and for environmental and stand structural variation (i.e. dominant tree height and basal area). Regenerating trees were mostly early‐successional species. Indigenous tree species regeneration was significantly higher in Grevillea plantations, where the seedling community also included late‐successional tree species. Regeneration under Eucalyptus was particularly poor. Acacia had a strong invasive nature, reducing its potential role and usefulness in indigenous forest restoration. Our study underlined that exotic tree plantations have differential effects on native tree species regeneration, with high potential for Grevillea plantations and low potential for invasive exotic species.     

Ecological outcomes of agroforests and restoration 15 years after planting

Large‐scale forest restoration relies on approaches that are cost‐effective and economically attractive to farmers, and in this context agroforestry systems may be a valuable option. Here, we compared ecological outcomes among (1) 12–15‐year‐old coffee agroforests established with several native shade trees, (2) 12–15‐year‐old high‐diversity restoration plantations, and (3) reference old‐growth forests, within a landscape restoration project in the Pontal do Paranapanema region, in the Atlantic Forest of southeastern Brazil. We compared the aboveground biomass, canopy cover, and abundance, richness, and composition of trees, and the regenerating saplings in the three forest types. In addition, we investigated the landscape drivers of natural regeneration in the restoration plantations and coffee agroforests. Reference forests had a higher abundance of trees and regenerating saplings, but had similar levels of species richness compared to coffee agroforests. High‐diversity agroforests and restoration plantations did not differ in tree abundance. However, compared to restoration plantations, agroforests showed higher abundance and species richness of regenerating saplings, a higher proportion of animal‐dispersed species, and higher canopy cover. The abundance of regenerating saplings declined with increasing density of coffee plants, thus indicating a potential trade‐off between productivity and ecological benefits. High‐diversity coffee agroforests provide a cost‐effective and ecologically viable alternative to high‐diversity native tree plantations for large‐scale forest restoration within agricultural landscapes managed by local communities, and should be included as part of the portfolio of reforestation options used to promote the global agenda on forest and landscape restoration.     

Scale‐dependent effects of forest restoration on Neotropical fruit bats

Neotropical fruit bats (family Phyllostomidae) facilitate forest regeneration on degraded lands by dispersing shrub and tree seeds. Accordingly, if fruit bats can be attracted to restoration sites, seed dispersal could be enhanced. We surveyed bat communities at 10 sites in southern Costa Rica to evaluate whether restoration treatments attracted more fruit bats if trees were planted on degraded farmlands in plantations or island configurations versus natural regeneration. We also compared the relative influence of tree cover at local and landscape spatial scales on bat abundances. We captured 68% more fruit bat individuals in tree plantations as in controls, whereas tree island plots were intermediate. Bat activity also responded to landscape tree cover within a 200‐m radius of restoration plots, with greater abundance but lower species richness in deforested landscapes. Fruit bat captures in controls and tree island plots declined with increasing landscape tree cover, but captures in plantations were relatively constant. Individual species responded differentially to tree cover measured at different spatial scales. We attribute restoration effects primarily to habitat structure rather than food resources because no planted trees produced fruits regularly eaten by bats. The magnitude of tree planting effects on fruit bats was less than previous studies have found for frugivorous birds, suggesting that bats may play a particularly important role in dispersing seeds in heavily deforested and naturally regenerating areas. Nonetheless, our results show that larger tree plantations in more intact landscapes are more likely to attract diverse fruit bats, potentially enhancing seed dispersal.     

Planting Design Effects on Avian Seed Dispersers in a Tropical Forest Restoration Experiment

Seed dispersal often limits tropical forest regeneration and animals disperse most rainforest tree seeds. This presents two important questions for restoration ecologists: (1) which animals are common seed dispersers? and (2) which restoration techniques attract them? Fourteen restoration sites were planted with four tree species in three designs, (1) controls (no planting, natural regeneration) (2) islands (trees planted in small patches), and (3) plantations (trees planted continuously over a large patch). We sampled birds in November, February, and April 2007–2008 with mist nets, in February and July 2009 with observations, and in July 2008 with both techniques. We documented 30 seed species from fecal samples of captured birds. All identified seed species were early‐successional forms. Four tanager species, three thrushes, two saltators, two flycatchers, and one finch were categorized as common seed dispersers, based on their high likelihood of dispersing seeds. Common dispersers were generalist species with small gape widths (<15 mm). Common dispersers were captured significantly more often in plantations than controls in most seasons and more often in plantations than islands during one season. Common disperser observations were significantly greater in plantations than controls during two periods and in plantations compared with islands in one period. Results indicate that plantation‐style planting is the conservative strategy to maximize attractiveness to common dispersers in tropical restoration sites. Island planting is an alternative when resources are limited although disperser activity may be lower in some seasons than in plantations. Additional research should investigate how to attract large, forest‐associated dispersers.     

Increase in nonnative understorey vegetation cover after nonnative conifer removal and passive restoration

Nonnative conifers are widespread in the southern hemisphere, where their use as plantation species has led to adverse ecosystem impacts sometimes intensified by invasion. Mechanical removal is a common strategy used to reduce or eliminate the negative impacts of nonnative conifers, and encourage native regeneration. However, a variety of factors may preclude active ecological restoration following removal. As a result, passive restoration – unassisted natural vegetation regeneration – is common following conifer removal. We asked, ‘what is the response of understorey cover to removal of nonnative conifer stands followed by passive restoration?' We sampled understorey cover in three site types: two‐ to ten‐year‐old clearcuts, native forest and current plantations. We then grouped understorey species by origin (native/nonnative) and growth form, and compared proportion and per cent cover of these groups as well as of bare ground and litter between the three site types. For clearcuts, we also analysed the effect of time since clearcut on the studied variables. We found that clearcuts had a significantly higher average proportion of nonnative understorey vegetation cover than native forest sites, where nonnative vegetation was nearly absent. The understorey of clearcut sites also averaged more overall vegetation cover and more nonnative vegetation cover (in particular nonnative shrubs and herbaceous species) than either plantation or native forest sites. Notably, 99% of nonnative shrub cover in clearcuts was the invasive nonnative species Scotch broom (Cytisus scoparius). After ten years of passive recovery since clearcutting, the proportion of understorey vegetation cover that is native has not increased and remains far below the proportion observed in native forest sites. Reduced natural regeneration capacity of the native ecosystem, presence of invasive species in the surrounding landscape and land‐use legacies from plantation forestry may inhibit native vegetation recovery and benefit opportunistic invasives, limiting the effectiveness of passive restoration in this context. Abstract in Spanish is available with online material.     

粤港澳大湾区不同恢复模式植物群落结构与生态系统健康的动态变化

基于长期定位监测数据,量化揭示了红锥纯林（Castanopsis hystrix）、10种与30种乡土树种混交林等3种乡土人工林植物群落的生物量、物种多样性、生物热力学健康水平（eco-exergy）和土壤理化性状在种植后13年内的发展动态,并与尾叶桉（Eucalyptus urophylla）纯林,以及自然恢复系统（灌草坡）进行了比较。结果表明：（1）研究期间,5种恢复模式的植物群落生物量均呈现波动上升趋势,但在发展节率上有所差异。13龄时的尾叶桉纯林与两种乡土树种混交林生物量显著高于其各自1龄时的水平,且显著高于自然恢复灌草坡;相较于其他人工林,红锥纯林生物量增长缓慢,但快于灌草坡;（2）5种恢复模式植物群落的物种多样性（物种丰富度、Shannon-Wiener指数、Pielou均匀度指数）在6至13龄间均呈下降趋势,且30种乡土树种混交林下降趋势最为显著。13龄时,两种混交林Shannon-Wiener指数略高于两种纯林,显著高于灌草坡;10种乡土树种混交林的Pielou均匀度指数略高于红锥纯林与30种乡土树种混交林,显著高于尾叶桉纯林与灌草坡。（3）4种人工林的植物群落生物热力学健康水平皆在6至13龄间显著增加;13龄时两种乡土混交林群落生态显著高于两种纯林,两种纯林显著高于灌草坡,且该差异主要源自于乔木层生态的差异。（4）不同植被恢复模式中,10种乡土树种混交林土壤养分的累积效果最佳,13龄时其土壤总氮含量显著高于红锥纯林和自然恢复灌草坡,但与30种乡土树种混交林和尾叶桉纯林无显著差异。（5）冗余分析结果显示,研究期间植被与土壤间的相关关系逐步建立,土壤理化性状对地上植被结构变化的解释度由1龄时的73.3%逐步上升至13龄时的82.0%,但只有土壤有机碳含量在13龄时与地上植被结构的相关性达到显著水平。上述结果表明,乡土种人工林与外来种人工纯林群落结构、生物热力学健康水平、及植被与土壤间关系的发展规律相似,且相对而言,混交林优于纯林,纯林优于自然恢复灌草坡。植被恢复的起始物种丰富度并不是越高越好;发展到13龄时,10种乡土树种混交林在植被结构与土壤改良方面均优于30种乡土树种混交林。植被与土壤间相关关系的建立是一个长期的过程,不同植被恢复模式对土壤理化性状的差异性影响难以在短期内有所显现。