元谋干热河谷地区新银合欢天然更新的初步调查

通过2005年6和10月对元谋干热河谷地区新银合欢人工林的调查,发现新银合欢林下幼苗数量较多,经过对幼苗刨根后,发现林下的新银合欢幼苗均为种子实生苗,表明新银合欢是通过种子繁殖来完成天然更新。新银合欢单株结实量在602~1513粒,树体高大的结实量多;其林下幼苗生长良好,更新密度最低为368株·m-2,最高达960株·m-2;新银合欢林缘幼苗最远扩散距离为58·3m,幼苗的扩散范围主要集中在距离林缘10m的区域内,种子受风力和流水的影响,可以沿沟谷传播很远。     

银合欢和苏门答腊金合欢根瘤菌的分离和回接

从银合欢和苏门答腊金合欢的根瘤各分离出三个快生型的根瘤菌,对其形态作了初步的观察。这些根瘤菌可能是同一族的,它们对其寄主植物进行回接和互接均能引起银合欢和苏门答腊金合欢结根瘤,互接形成的根瘤形态与寄主植物的根瘤相同;箭舌豌豆和武宁苕子的根瘤菌不能引起银合欢和苏门答腊金合欢植株结根瘤;分离得到的根瘤菌对银合欢和苏门答腊金合欢均有反馈的增益作用,几个生物学指标均比对照的高;在无菌条件下,全氮培养抑制了根瘤菌对寄主植物结瘤,琼脂固体培养的植株根瘤固氮活性比沙培、水培的高。     

惠安县引种苏门答腊金合欢初报

苏门答腊金合欢[Acacia glauca(L.) Moench]原产西印度群岛。热带地区广泛引种。苏门答腊金合欢具有较强的固氮能力,生长迅速,萌蘖力强,是作薪炭林、紫胶寄主树、饲料和绿肥等多种用途的树种。     

植被恢复对干热河谷退化土壤改良的影响

土地退化和土壤恶化是我国干热河谷主要环境问题。树种筛选及树种与土壤关键限制因子间的相互作用是生态恢复的基础和前提。对比研究了干热河谷地区植被恢复22年间不同时期(1991、1997、2005和2013年)5种人工林(新银合欢Leucaena leucocephala,苏门答腊金合欢Albizia kalkora,大叶相思Acacia auriculiformis,印楝Azadirachta indica和赤桉Eucalyptus camaldulensis)和1种自然恢复样地中土壤主要物理、化学和微生物性质。结果表明植被恢复处理和取样时间对土壤性质有显著影响。在22a的植被恢复期内,土壤物理性质提高幅度为3.0%—20.2%,远不及土壤微生物和化学性质。通过自然恢复机制改良的退化土壤,其改良率(63.6%)高于印楝(54.9%)、苏门答腊金合欢(54.3%)和赤桉(53.2%)人工林,但改良率不及新银合欢(68.2%)和大叶相思(67.3%)人工林。研究得出造林树种类型决定干热河谷土壤改良进程。与自然恢复相比,人工植被恢复(如造林)并不一定能加速退化土壤改良。新银合欢和大叶相思适合作为改良干热河谷退化土壤的先锋树种,而生态系统自然恢复也可作为改良干热河谷退化土壤的一种适宜方式。     

苏门答腊金合欢群落生物量和凋落物量的研究

本文从群落生态学的角度探讨了厦门地区苏门答腊金合欢人工群落的生物量和凋落物量等生态特征。1． 5年生苏门答腊金合欢群落总生物量为81t·ha-1,平均年净生产量为16.2t·ha-1;秋季消光系数为0.52;年均光能利用率为0.56%。运用生物量基径二次相关方程,可估测该群落的生物量。2． 5年生苏门答腊金合欢群落年凋落物量为7.9t·ha-1。年凋落物中氮、磷和钾的含量分别为152.1、32.3和26.0kg·ha-1。 凋落叶中的氮、磷和钾含量均高于同一生境中先锋树种台湾相思和马尾松凋落叶中的相应指标,且其凋落物的分解速率高。     

元谋干热河谷不同人工林中鞘翅目甲虫多样性比较

在元谋干热河谷采用网扫法调查了云南松林、桉树林、新银合欢林、桉树＋新银合欢林、印楝林及多树种混交的人工林鞘翅目昆虫多样性。结果表明,鞘翅目甲虫标本925号,计71种,分属18个科,其中叶甲科种类最丰富,象甲科数量最丰富。人工林鞘翅目昆虫群落物种丰富度在7～23,Shannon—Wiener多样性指数在1．249～2．562,昆虫多样性总体较低。各样地鞘翅目群落之间为不相似水平。云南松林鞘翅目昆虫群落物种丰富度、Shannon—Wiener指数、Simpson指数及Pielou指数分别为20、2．562、0．104和0．855,其多样性最高,多树种混交林较高,印楝林较低,而桉树林、新银合欢林、桉树＋新银合欢林多样性极低。多树种混交的恢复对昆虫多样性提高有显著促进作用。     

银合欢和“新银合欢”

近年来,在国内一些书刊、树木(苗木)名录上,把Leucaena glauca(Willd.)Benth.称为银合欢;而把L.leucocephala(Lam.)de Wit称作“新银合欢”。把这两个拉丁学名看成是两种植物是不对的,它只是异名与正名的关系,所谓“新银合欢”,实际上就是银合欢。此外,还有中名冠以地名的银合欢,如“萨尔瓦多(新)银合欢”、“菲律宾银合欢”等,也都是银合欢这个种,只不过是类型、品系或来源地不同而已。     

银合欢幼苗根瘤固氮特性研究

银合欢(Leucaena leucocephala)是热带亚热带豆科木本植物,生长迅速,用途广泛。可作为薪炭、用材、饲料、绿肥及水土保持林栽培,是我国华南地区农林牧生产上有希望的树种。本文对银合欢幼苗生长过程中根瘤发育     

树种多样性对亚热带米槠林细根生物量和形态特征的影响

采用土芯法获取福建省三明市米槠人工林、米槠人促更新林和米槠天然更新林的细根(直径2 mm),研究树种多样性对细根生物量、垂直分布及形态特征的影响.结果表明:米槠人工林、米槠人促更新林和米槠天然更新林0~80 cm土层的细根生物量分别为(182.46±10.81)、(242.73±17.85)和(353.11±16.46)g·m-2,细根生物量随树种多样性的增加呈增加趋势.3种米槠林分0~10 cm土层细根生物量占细根总生物量的35%以上,各林分细根生物量均随土层变化显著.林分类型和土层深度对细根分布没有显著的交互作用,表明树种多样性的增加没有引起米槠林细根空间上的生态位分化.3种米槠林细根的根表面积密度和根长密度均以米槠天然更新林最高,米槠人工林最低.比根长的大小顺序为米槠人促更新林米槠人工林米槠天然更新林,比表面积的大小顺序为米槠天然更新林米槠人工林米槠人促更新林,林分类型和土层的交互作用对二者均无显著影响,表明林分水平的细根形态可塑性对树种多样性响应不显著.     

三峡库区新银合欢引种栽培试验

引言新银合欢(Leucaena leucocephla cv. Salvadot)又名萨尔瓦多银合欢,是一种重要的热带木本豆科植物,是大有发展前途的饲料、肥料、燃料和木料的多用途树种。据报道第一年可生长2米以上,以后每年生长1米以上。在没有冻害和立地条件好的地     

川西亚高山65年人工云杉林种子雨、种子库和幼苗定居研究

川西亚高山人工针叶林已成为亚高山森林的重要组成部分, 它们是否具有持续的自然更新能力, 是决定川西亚高山针叶林群落演替方向和维持该区针叶林大面积存在的基础。以川西米亚罗亚高山人工云杉(Picea asperata)林(65 a)为研究对象, 对种子雨量年际变化、土壤种子库动态、种子萌发和幼苗定居等更新过程的关键环节进行了连续7年(2002-2008年)的野外观测, 以研究人工云杉林更新潜力及影响其更新的限制因素。结果表明: 该区云杉林种子雨一般从每年的10月初开始下落, 一直到翌年的1月底或2月初结束; 云杉种子散落存在明显的大小年现象, 种子散落周期为4年, 且大小年之间种子产量差异极大; 云杉种子从下落到土壤到种子完全失去活力不到1年时间, 属于Thompson和Grime定义的第II类土壤种子库类型。腐烂死亡和动物取食是土壤种子库损耗的主要因素, 而种子通过萌发真正转化为幼苗的比例非常低, 仅占2002年下落种子总量的3.6%。种子萌发后, 环境筛的作用导致云杉幼苗大量死亡, 尤其是在种子萌发后的一个生长季节内, 其死亡率高达78%。凋落物和苔藓是构成人工云杉林下地表的两种主要地被物类型, 二者占所有调查幼苗数量的93%左右; 两种地被物类型上0-2 cm层幼苗存活率最高, 分别占存活幼苗总数的76.07%和86.72%, 随地被物厚度增加, 幼苗存活率呈明显下降趋势, 而幼苗死亡率呈明显升高的趋势, 表明林下地被物厚度也是影响云杉幼苗定居的重要因素。两种地被物对幼苗生长的影响不同, 除株高之外, 分布在苔藓上的云杉幼苗生长参数(地径、分枝数、干重以及干重年增长率)明显高于分布于凋落物上的幼苗, 表明苔藓地被物更有利于云杉幼苗定居。尽管该区大量云杉种子下落, 但由于种子的高损耗率、幼苗的低输出率以及萌发幼苗的高死亡率, 使得人工云杉林下种子通过萌发转为实生幼苗的数量非常少, 最终真正能补充到云杉种群的个体数量非常有限。     

Comparisons of food availability and group density of Japanese macaques in primary, naturally regenerated, and plantation forests

We compared food availability and group density of Japanese macaques in Yakushima, southern Japan, among primary forest and two habitats that had been disturbed by logging and had different regeneration histories. The study was conducted in an undisturbed national park, forest that was logged 7-18 years ago and later naturally regenerated, and forest that was logged 19-27 years ago and later planted with Japanese cedar (Cryptomeria japonica) trees. The plantation forest was primarily composed of large Cryptomeria japonica trees at low stand density, while the naturally regenerated forest was composed of many small trees. The total basal area and number of trees in the primary forest were comparable to those in the plantation forest. Annual fruit production was greatest in the naturally regenerated forest, intermediate in the primary forest, and negligible in the plantation forest. Herb availability was high in the naturally regenerated forest, but low in the primary and plantation forests. The group density of Japanese macaques was high in the naturally regenerated forest, intermediate in the primary forest, and low in the plantation forest. Since group size in the naturally regenerated forest was small, individual density was almost the same as in the primary forest. These results suggest that the effects of regeneration on macaques vary between the two habitats. The plantation forest consisted mostly of Cryptomeria japonica, which supplies only flowers as food in a limited season, and had a lower density of macaques. On the other hand, in the naturally regenerated forest, fruit production and herb availability were high (probably because of the enhanced light conditions after logging), and the density of macaques was as high as in the primary forest.     

Regeneration of planted conifers across climatic moisture gradients on the Canadian prairies: implications for distribution and climate change

The influence of dry climates on white spruce ( Picea glauca (Moench) Voss)) regeneration was examined by conducting surveys of seedlings and small trees that had regenerated naturally at 100 farm shelterbelts and plantations in southern Saskatchewan, Canada. The sites surveyed were located along a climate moisture gradient extending from the relatively moist boreal forest, across the aspen parkland, to the semi-arid prairie grasslands. Natural regeneration was greatest at sites in the boreal forest and northern aspen parkland, decreased in the southern aspen parkland, and was negligible in the grassland zone. Furthermore, the few seedlings found in the drier zones were usually in poor condition. Similar results were obtained for the introduced Colorado spruce ( Picea pungens Engelm.) and Scots pine ( Pinus sylvestris L.). It is concluded that the present climate of the southern parkland and grassland is too dry to permit natural regeneration of white spruce and other conifers. If increases in atmospheric CO₂ levels lead to a drier future climate in the southern boreal forest of western Canada, the ability of conifers to regenerate naturally may be significantly reduced.     

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.     

Stand structure and natural regeneration of degraded forestland in the northern mountainous region of Vietnam

Vietnam experienced significant alterations of forest environments during the last half of the twentieth century, and reforestation efforts have increased since the 1990s. This study developed comparisons of naturally regenerated and plantation forestlands in northern Vietnam in order to gain a better understanding of reforestation options for the dual objectives of biodiversity and commercial tree production. Stand structure of secondary natural forest after logging and shifting cultivation were investigated at two study sites (Hoa Binh Province and Phu Tho Province). Natural regeneration of seedlings between the secondary natural forests and nearby mixed species plantations were measured and compared. The dominant tree species consisted of Aporosa villosa, Ficus racemosa, Machilus bonii and Vernicia montan at the Hoa Binh site and Cinnamomum parthenoxylum, Ormosia balabsae and Lithocarpus gigantophyllus at the Phu Tho site, which are mostly pioneer species. The secondary natural forests had higher abundance and diversity indices of seedlings than the mixed species plantations. Soil fertility of the secondary natural forests was better than that of the mixed species plantations (P < 0.05). An important finding is that, for the study sites examined, secondary natural forest resulted in more diverse and better-stocked forests than plantation forestry, implying that in areas where reforestation is undertaken the silvicultural potential of natural regeneration should not be underestimated.     

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.     

杉木人工林种子雨组成和季节动态

杉木人工林已成为亚热带森林的重要组成部分,它具有可持续的自然更新能力,是决定杉木林群落演替方向和维持杉木林大面积存在的基础.本文以杉阔混交林和杉木纯林为研究对象,分析其种子雨的物种组成、数量大小和季节动态,以及林分优势物种种子雨数量特征和季节变化,揭示种源条件是否是制约杉木人工林天然更新的主要因素.结果表明:杉阔混交林和杉木纯林分别收集到13科18属21种和12科16属19种的种子.混交林和纯林的所有物种种子雨强度分别为3797和3300粒·m^-2.乔木物种种子数量在种子雨中占绝对优势,混交林占89.1%,纯林占86.2%,其中杉木种子数量最多,其完整种子雨强度分别为825和345粒·m^-2.两林分种子雨各类型种子所占比例均为完整种子>干瘪或腐烂种子>被取食种子.两林分种子雨均具有明显的季节动态,均在秋季到达高峰,且在落种高峰期种子雨以完整种子为主.无论是杉阔混交林还是杉木纯林都有充足的种源,种源(种子雨)条件不是制约杉木林天然更新的主要因素.     

Litterfall and nutrient dynamics shift in tropical forest restoration sites after a decade of recovery

Multi‐year studies comparing changes in litterfall biomass and nutrient inputs in sites under different restoration practices are lacking. We evaluated litterfall dynamics and nutrient inputs at 5 yr and after a decade of recovery in four treatments (natural regeneration—no planting, plantation—entire area planted, tree islands—planting in patches, and reference forest) at multiple sites in an agricultural landscape in southern Costa Rica. We inter‐planted two native species (Terminalia amazonia and Vochysia guatemalensis) and two naturalized N‐fixing species (Inga edulis and Erythrina poeppigiana) in plantation and island treatments. Although litterfall N was higher in plantations in the first sampling period, litter production and overall inputs of C, N, Ca, Mg, P, Cu, Mn, and Fe did not differ between island, plantation, or reference forest after a decade; however, all were greater than in natural regeneration. Potassium inputs were lower in the natural regeneration, intermediate in island and plantation, and greater in reference forest. The percentage of litterfall comprised by the N‐fixing planted species declined by nearly two‐thirds in both plantations and islands between sampling periods, while the percentage of V. guatemalensis more than doubled, and the percentage from naturally regenerated species increased from 27 to 47 percent in islands. Island and plantation treatments were equally effective at restoring litterfall and nutrient inputs to levels similar to the reference system. The nutrient input changed substantially over the 7‐yr interval between measurements, reflecting shifts in vegetation composition and demonstrating how rapidly nutrient cycling dynamics can change in recovering forests.     

中亚热带不同森林更新方式生态酶化学计量特征

了解土壤生态化学计量特征对预测不同生态系统养分变化、功能以及植物生产力具有重要意义。森林更新是维持中亚热带森林生态系统可持续发展的重要手段。选取福建省三明市陈大林业采育场3种不同森林更新方式进行研究,包括米槠次生林（SF）、米槠人工促进天然更新林（AR）和杉木人工林（CF）,测定其土壤理化性质及土壤3种酶,计算酶化学计量。结果显示：1）AR的土壤总氮、全磷、铵态氮含量以及含水量最高（P < 0.05）,土壤有效磷的含量则是CF最高（P < 0.05）;2）生态酶化学计量结果表明AR的土壤微生物处于氮限制状态,CF的土壤微生物处于磷限制状态;3）冗余分析表明,土壤含水量和铵态氮是驱动不同森林更新方式土壤生态酶化学计量变异的重要环境因子。研究表明,人促更新方式更有利于土壤有效氮的积累,而人工林则有利于土壤有效磷积累,这可能与造林树种有关。土壤生态酶化学计量更易受到土壤含水量以及有效性养分的驱动,而与土壤化学计量未呈现良好的耦合性。     

樟子松人工固沙林天然更新特征

采用比较分析与野外调查的方法。对沙地樟子松人工林天然更新特征进行了研究,能够进行天然更新的引种地区天然更新在时间上是不连续的,与特定年份的某些降水因子密切相关;在空间上主要有3种更新方式;林隙更新,林缘更新,阔叶林下更新;天然更新幼树生长情况与人工林的生长差异不大。