大兴安岭北坡火烧迹地森林郁闭度恢复及其影响因子

1987年发生在大兴安岭北坡的特大森林火灾,总过火面积达1.33×106 hm²,形成了各种火烧强度区与未火烧区构成的异质镶嵌体。火烧强度、地形以及火后人类的恢复干预都不同程度地对火后森林恢复产生了影响。研究目的有二：一是为了揭示火后森林恢复状况;二是探寻火烧强度、地形以及火后更新措施等因素对火后森林恢复的影响程度。选取了位于火烧区的图强林业局中部的育英和图强两林场为研究区,选取反映森林景观质量的郁闭度指标作为研究对象,利用地理信息系统软件,将1987年火前与2000年的郁闭度等级分布图叠加,分析火后森林质量的恢复状况;利用多元线性回归法对火烧强度、海拔、坡度、坡向、坡位等地形因子以及各种更新方式对郁闭度恢复的影响程度进行了定量研究。结果显示,2000年郁闭度等级与火前相比发生了明显变化,2000年各林型郁闭度优势等级均由较高的等级4,5降为等级3;而等级1的比重也有所降低。表明,火后森林总体生长状况良好,无林地比重降低,但由于恢复时间较短,具有较高郁闭度的森林所占比重仍较低。多元线性回归显示,各因子均对火后郁闭度恢复产生了显著性影响。其中,海拔影响最大,与郁闭度等级呈正相关;其次是火烧强度,呈负相关;其它地形因子以及更新方式影响较小。     

大兴安岭北坡火烧迹地森林郁闭度恢复及其影响因子

1987年发生在大兴安岭北坡的特大森林火灾,总过火面积达1.33×106hm2,形成了各种火烧强度区与未火烧区构成的异质镶嵌体。火烧强度、地形以及火后人类的恢复干预都不同程度地对火后森林恢复产生了影响。研究目的有二：一是为了揭示火后森林恢复状况;二是探寻火烧强度、地形以及火后更新措施等因素对火后森林恢复的影响程度。选取了位于火烧区的图强林业局中部的育英和图强两林场为研究区,选取反映森林景观质量的郁闭度指标作为研究对象,利用地理信息系统软件,将1987年火前与2000年的郁闭度等级分布图叠加,分析火后森林质量的恢复状况;利用多元线性回归法对火烧强度、海拔、坡度、坡向、坡位等地形因子以及各种更新方式对郁闭度恢复的影响程度进行了定量研究。结果显示,2000年郁闭度等级与火前相比发生了明显变化,2000年各林型郁闭度优势等级均由较高的等级4,5降为等级3;而等级1的比重也有所降低。表明,火后森林总体生长状况良好,无林地比重降低,但由于恢复时间较短,具有较高郁闭度的森林所占比重仍较低。多元线性回归显示,各因子均对火后郁闭度恢复产生了显著性影响。其中,海拔影响最大,与郁闭度等级呈正相关;其次是火烧强度,呈负相关;其它地形因子以及更新方式影响较小。     

茂县土地岭植被恢复过程中物种多样性动态特征

植被恢复是退化生态系统重建的重要途径,植被恢复过程物种多样性的变化反映了植被的恢复程度.通过群落调查和多样性分析,研究了岷江上游土地岭植被恢复过程中群落物种多样性特征.结果表明： 恢复过程中6类不同类型群落分别表现其对于不同环境特征、干扰及更新方式等的响应;森林是较灌丛更适合当地环境状况的植被类型;人工恢复无干扰和轻度干扰群落的多样性相对较高,是较好的恢复模式.重度干扰使得1年生植物与地下芽植物比例增加,其它口食性较好的多年生草本减少.较强的干扰是群落无法更新、长期处于灌丛阶段且多样性较低的重要原因.本地区人工恢复群落在更新进程和多样性维持上优于自然更新群落,种植华山松加速了本地区植被演替进程.建议以适合恢复区域的多种恢复配置方式进行造林,并避免较强干扰,可以加速群落演替进程并保持恢复群落较高的物种丰富度与多样性.     

川西亚高山森林恢复的空间格局分析

以米亚罗林区为例,利用森林样地调查和遥感影像解译方法,通过森林植被图与数字地形的叠加,分析了川西亚高山森林大规模采伐和更新后,主要森林植被类型外貌与起源之间的联系,以及各类型分布的地形分异规律和空间格局.结果表明,大规模采伐和更新后,森林植被类型的外貌与起源相关,老龄针叶林为保留下来的原始林,中幼龄针叶林为人工林,落叶阔叶林为天然次生林,而针阔混交林中既有天然次生的成分,也有人工、天然更新共同作用的成分.海拔2 800~3 600 m是米亚罗的主要伐区,森林恢复表现出坡向分异:人工更新的中幼龄针叶林主要分布于阳坡、半阳坡;落叶阔叶林和针阔混交林受天然更新的影响,主要分布于阴坡、半阴坡.老龄针叶林主要保留在海拔3 600 m以上.恢复过程中各种森林植被类型镶嵌分布,景观破碎化严重.     

川西亚高山森林恢复的空间格局分析

以米亚罗林区为例,利用森林样地调查和遥感影像解译方法,通过森林植被图与数字地形的叠加,分析了川西亚高山森林大规模采伐和更新后,主要森林植被类型外貌与起源之间的联系,以及各类型分布的地形分异规律和空间格局.结果表明,大规模采伐和更新后,森林植被类型的外貌与起源相关,老龄针叶林为保留下来的原始林,中幼龄针叶林为人工林,落叶阔叶林为天然次生林,而针阔混交林中既有天然次生的成分,也有人工、天然更新共同作用的成分.海拔2 800～3 600 m是米亚罗的主要伐区,森林恢复表现出坡向分异:人工更新的中幼龄针叶林主要分布于阳坡、半阳坡;落叶阔叶林和针阔混交林受天然更新的影响,主要分布于阴坡、半阴坡.老龄针叶林主要保留在海拔3 600 m以上.恢复过程中各种森林植被类型镶嵌分布,景观破碎化严重.     

鸟类栖木在森林植被恢复中的生态意义

鸟类传播种子对于植物种群自然更新及群落演替具有重要的生态意义,鸟类栖息的树木具有富集种子雨功能,在山体滑坡区及废弃矿区等干扰生境中人工设置鸟类栖木,可以增加鸟类传播的种子雨输入,丰富土壤种子库,尤其食果鸟类可以传播那些处于群落演替中期至后期的乔、灌木树种,能够促进受干扰地区森林植被的演替进程.5·12汶川大地震对地震灾区造成了大面积的山体滑坡和严重的植被破坏,在地震灾区森林植被的生态恢复工作中,一些地区可以采用人工设置鸟类栖木方法,充分利用山体滑坡区周围残余森林的丰富种子源及众多食果鸟类,促进灾区森林植被的自然恢复.     

Impact of forest fire on soil seed bank composition in Himalayan Chir pine forest

了解植物群落火烧后的再生策略对于解释其如何应对喜马拉雅次生林中反复发生的人为森林火灾非常重要。本研究的主要目的是了解：1)火烧如何影响土壤种子库组成; 2)森林火灾后土壤种子库组成与立地植被的差异有多大。在森林火灾发生后,立即从火烧和相邻的未火烧地点收集土壤样本,并在净室中培养,以便出苗。在季风气候后期/初秋季节,我们再次探访这些地点,以了解森林火灾后恢复的植被的物种组成。研究结果表明,土壤中含有>70种的植物种子。火烧区和未火烧区种子库平均密度分别为8 417和14 217粒/m²,且均随土层深度的增加而减少。整体的火烧对种子密度无显著影响;但是,如果考虑土层因素,火烧只对最上层土壤的种子密度有显著影响。土壤种子库和立地植被的物种丰富度分别为73和100 (共有物种数为35),相似性约为40%。而在火烧区和未火烧区发现土壤种子库中>80%的物种相似。另外,火烧区(87)和未火烧区(78)立地植被的物种丰富度没有显著差异。本研究表明,火烧对土壤种子库组成和种子恢复潜力的影响不显著。下层草本植物和灌木植物群落有能力形成一个抗火烧的、有活力的土壤种子库,并有能力在火灾后的雨季恢复,这些发现也解释了它们是如何在维持其种群的同时减少了重复火灾带来损害的风险。     

塔河林业局林火对植被的影响

针对大兴安岭地区塔河林业局不同林型下,不同火烧强度的火烧迹地的森林植被更新及恢复情况进行了调查研究。结果表明：（1）针叶林过火迹地上,落叶松幼苗较少,阔叶树萌条更新强度同火烧程度成正比;火烧前生长有白桦、赤杨的林地上,火烧后阔叶树成为主导树种,林相完全发生变化。（2）重度火烧下有利于天然更新,促使白桦、山杨萌生。中度火烧最初形成以杨桦为优势树种的阔叶林,后逐渐演变为针阔混交林。轻度火烧有利于针叶林的更新。（3）火烧后不同林型下灌木草本植被种类变化不同。从盖度方面来看,杜鹃落叶松林型中林下灌木草本更新最为良好。     

大兴安岭火烧迹地不同恢复方式碳储量差异

为了探讨不同恢复方式对大兴安岭重度火烧迹地碳储量的影响,以人工恢复(兴安落叶松、樟子松)和天然恢复的林分为研究对象,采用干烧法对乔木层、灌木层、草本层和枯枝落叶层含碳率进行测定.采用全收获法和平均标准木法获得林分各组分生物量估算森林植被的碳储量,分析不同恢复方式下林分各组分碳储量的分配特征.结果表明： 人工恢复和天然恢复的林分灌木层平均含碳率高于乔木层和草本层.兴安落叶松人工林灌木层平均含碳率为45.8%、枯枝落叶层为45.3%、乔木层为44.4%、草本层为33.6%.樟子松人工林灌木层和乔木层平均含碳率高于50%.天然次生林乔木层、灌木层和枯枝落叶层平均含碳率在42%左右.森林植被层中,生物量贡献率从大到小依次为乔木层、灌木层和草本层.兴安落叶松人工林森林植被层和枯枝落叶层生物量总和为123.90 t·hm^-2,远高于樟子松人工林和天然次生林.火烧后人工恢复23年的兴安落叶松人工林森林植被碳储量为50.97 t·hm^-2,其中,乔木层碳储量为49.87 t·hm^-2,占森林植被层总碳储量的97.8%,草本层所占比重仅为0.02%.人工恢复的林分植被层总碳储量高于天然恢复的林分,火烧迹地在这一时段内采用人工恢复的方式较天然恢复碳汇能力更强.     

桂西北喀斯特人为干扰区植被自然恢复22年后群落特征

采用全面调查和样方调查的方法,以坡面为尺度,以顶极群落为对照,运用干扰理论和多样性分析方法,研究了桂西北喀斯特4类典型干扰区自然恢复22a之后植被特征及空间分布的变化。结果表明,干扰区的物种多样性丧失严重,共出现维管束植物91科206属241种,仅有自然保护区的26．6％,6种植被类型的顺向演替系列为石漠化稀疏草丛→草丛→灌丛→藤刺灌丛→落叶阔叶林→常绿落叶阔叶混交林片段。随着坡位的上升,群落的高度、盖度、生物量和物种多样性急剧下降。密度则呈少、多、次少的单峰分布状态,各项指标均远低于自然保护区。不同干扰方式对植被自然恢复的影响不同,其中整坡火烧＋垦殖的破坏性最大,呈现了石漠化景观,整坡火烧＋放牧次之,采樵属选择性干扰,采樵＋放牧＋坡脚火烧的恢复相对较快,没有放牧干扰的采樵＋坡脚火烧恢复更好。此外还针对性地提出了桂西北喀斯特干扰区在不同立地类型上人工与自然相结合的4条植被恢复途径。对因各种人为干扰导致的桂西北喀斯特生态系统处于极度退化状态下的植被恢复建设和生态重建具有重要的理论价值和实际意义。     

1987年大兴安岭特大火灾后北坡森林景观生态恢复评价

通过空间直观景观模型(LAND IS)来探讨大兴安岭北坡1987年特大森林火灾后,在目前这种恢复方案下以及完全依靠天然更新下森林景观的长期动态,通过对比研究来评价目前所采取的恢复措施是否能够有效地恢复森林资源。研究结果表明:1987年大火后所采取的恢复措施可以在很大程度上增加针叶树种在该区所占的比例,而相应地降低阔叶树种的比重。由于在目前的恢复措施下,不仅大面积地种植针叶树种,同时也采伐了大量的成、过熟林,使落叶松和樟子松的蓄积量在开始阶段不仅没有增加,反而有大幅度的下降。但最终,所更新的幼苗逐渐成材,落叶松和樟子松的蓄积量逐渐超过天然更新下的。在演替前期,白桦的蓄积量在这2种模拟方案下相差不大;而在演替后期,白桦在天然更新方案下的蓄积量要高于在目前恢复措施下的蓄积量。另外,物种在不同的区域的变化动态又有较大的差异。在重度火烧区,由于人为种植大量的针叶树种,使它们所占的面积比例明显高于完全依靠天然更新下其在重度火烧区所占的比例;而阔叶树种则相反,在完全依靠天然更新方案下所占的面积百分比明显高于在目前恢复方案下的比例。而在未火烧和轻中度火烧区,由于火后人为采伐大量的落叶松和樟子松,使这2个树种在该区所占的比例在开始100多年里要低于完全依靠天然更新下的比例,随后逐渐高于天然更新下所占的比例,但相差不大;阔叶树种则正好相反。另外,目前恢复方案不仅极大地改变了主要物种在该区所占的比例,而且还明显的影响了它们的空间分布格局。     

Site quality effects on post‐fire regeneration of Pinus brutia forest on a Greek island

Abstract. Natural stands of Pinus brutia were compared to burned areas after a great fire in 1985 on the island of Thasos, North Greece, in relation to site quality effects on the success of natural regeneration and understorey vegetation. The number of seedlings in the natural stands of P. brutia was 1124/ha against 3188/ha in the burned area. In both cases natural regeneration was successful. Under the canopy of P. brutia forests the predominant shrubs were Quercus coccifera and vPhillyrea latifolia. A high percentage (up to 40%) of the total area was covered by these species. In the burned areas, 12 yr after the wildfire of 1985, Cistus incanus and C. salvifolius played a significant role in the survival of P. brutia seedlings. These species had covered the burned area long before the pine seed germination.     

干旱区荒漠景观的植被自然更新机制初探

根据实地调在和参阅资料．依山前洪积扇、河流沿岸阶地、沙丘及丘间低地、戈壁、盐沼的景观斑块,初步探讨干旱区植被的自然更新机制。干旱区的高温干燥、温差强烈、风蚀沙埋已成为植物繁衍后代的动力;萌蘖、劈裂、地下茎萌生等多种繁殖方式．使荒漠植物在严酷的条件下实现自然更新,形成以母株为中心的母系居群。地貌形态和种子传播动力决定了群落外形。在干旱区,以种子繁殖的植物之种子成熟期与年内的丰水期相吻合,有利于植被更新．只有在连续2年降水较大时（超过多年平均降水量）,沙丘和丘间地,戈壁植被的自然更新才可能发生;河流沿岸植被的自然更新受地下水影响最明显;湖盆盐碱地植被带有水生植被的痕迹,自然更新相对较难;景观斑块镶嵌分布．形成微环境均异的廊道．有利于植被的自然更新。     

Influence of Post‐Clearing Treatment on the Recovery of Herbaceous Plant Communities in Amazonian Secondary Forests

Secondary forests are an increasingly common feature in tropical landscapes worldwide and understanding their regeneration is necessary to design effective restoration strategies. It has previously been shown that the woody species community in secondary forests can follow different successional pathways according to the nature of past human activities in the area, yet little is known about patterns of herbaceous species diversity in secondary forests with different histories of land use. We compared the diversity and abundance of herbaceous plant communities in two types of Central Amazonian secondary forests—those regenerating on pastures created by felling and burning trees and those where trees were felled only. We also tested if plant density and species richness in secondary forests are related to proximity to primary forest. In comparison with primary forest sites, forests regenerating on non‐burned habitats had lower herbaceous plant density and species richness than those on burned ones. However, species composition and abundance in non‐burned stands were more similar to those of primary forest, whereas several secondary forest specialist species were found in burned stands. In both non‐burned and burned forests, distance from the forest edge was not related to herbaceous density and species richness. Overall, our results suggest that the natural regeneration of herbaceous species in secondary tropical forests is dependent on a site's post‐clearing treatment. We recommend evaluating the land history of a site prior to developing and implementing a restoration strategy, as this will influence the biological template on which restoration efforts are overlaid.     

植物自然更新研究进展

植物自然更新是一个复杂的生态学过程,它对种群的增殖、扩散、延续和群落稳定及演替具有重要的作用,是植被动态研究的热点。目前国内外在这方面的多数研究主要从更新过程中的某一或几个阶段入手,分析各生态因子对更新的影响,或从林窗、火烧、动物等干扰对自然更新影响的角度揭示植被自然更新的机制。本文从植物自然更新方式、干扰对更新的影响及群落的更新等方面进行了总结,并提出了今后该领域的研究建议。     

Comparison of regeneration following burning,clearing or mineral sand mining at Tomago,NSW: I. Structure and growth of the vegetation

Abstract We have begun a long-term ecological research project to address questions about the impact of multiple disturbances on the species richness of communities and whether multiple disturbances are additive or interactive. A protected water catchment area was chosen, which is subjected to fires, sand mining and clearing, and for which detailed records are available. The study area, at Tomago (32°52′S, 151°45′E), has forest, woodland, shrubland and swamp on a sand substrate, with the vegetated dunes forming part of a coastal embayment. Forty-four sites were located in forested areas that had undergone disturbance by either fire, sand mining or clearing. Sites of each disturbance type were grouped into four age classes: less than 1 year since disturbance, nominally 1991; 5 years, nominally 1986; 11 years, nominally 1980; and 17 years, nominally 1974. A set of burned sites, with the time of the last fire matched to the times of the other disturbances, was used as the control response. In this paper we describe the study area and sites, then examine the effects of each single disturbance on vegetation structure. Canopy cover increased with time and type of disturbance, with 17 year old cleared or mined sites similar to the cover of 11 year old burned sites. In the first two years after disturbance, burned sites had significantly more understorey vegetation than cleared or mined sites, but by 5 years all three were similar. The data presented here show that regeneration of mined sites at Tomago is substantially slower than regeneration following disturbance by fire, with the regeneration of cleared sites intermediate but closer to mining than fire. After 17 years regeneration, cleared and sand mined sites had not returned to the vegetation structure of the pre-disturbance state. Understorey height and the amount of vegetation on cleared or mined sites have not achieved the levels in the original forest, although canopy cover did seem to have reached pre-disturbance levels. Current rehabilitation techniques are more sophisticated than those used 17 years ago and continued monitoring of sites currently being rehabilitated may show a faster return to pre-disturbance states. Having established the hierarchy and nature of the response to each single disturbance here, we are now in a position to investigate the impact of multiple disturbances.     

地形对大兴安岭北坡林火迹地森林景观格局影响的梯度分析

198 7年大兴安岭“5 .6”特大森林火灾 ,过火面积 1.33× 10 6 hm2 。火后 ,不同的火烧强度区和岛状的未火烧区形成了一个异质镶嵌体 ,然而在自然演替和人为干扰作用下 ,十几年过去之后这种异质镶嵌体格局已经发生了明显变化。以大兴安岭北坡 ,图强林业区的育英和奋斗两个林场为研究区 ,总面积 1.2× 10 5hm2 ,在景观尺度上 ,以遥感和地理信息系统为技术手段 ,将地形因子进行梯度划分 ,并运用分布指数和偏相关分析探讨了大兴安岭在 1987年大火后森林景观在地形梯度上的变化情况。研究结果表明 :森林景观在地形梯度上的格局发生了明显的变化 ,但是不同的景观斑块类型变化幅度不同 ,不同的地形因子对不同森林景观斑块类型变化的影响强度也迥异 ;偏相关分析表明地形对主要森林景观斑块类型之间的变化影响最大的是坡度 ,其次是海拔 ,坡向的影响不明显。     

Landform effects on fire behavior and post-fire regeneration in the mixed forests of northern Japan

This study was conducted to clarify the characteristics of landform effects on fire behavior and post-fire regeneration and to examine regional differences in the effects of fire within a mixed-forest area with various topographic conditions in Hokkaido, northern Japan. Fire spread was controlled by topographic barriers such as ridges and valleys, although this was not clear in the areas with serpentinite. Fire frequency was higher on windward slopes of the prevailing wind, and the size of the burned area varied with the underlying geology, which controlled the areal extent of hillside slopes. In areas with terrace deposits, Wakkanai Formation or serpentinized rock, burned areas were large and included few unburned stands. The type of vegetation that grew following the fires varied with slope aspect and topographic position.Sasa grasslands often formed at wind-exposed sites. The grasslands were well developed in the three areas with the previously mentioned geology, where large-scale burning had occurred. Structure of the re-established forest stands was also affected by landforms. Canopy height and the maximum diameter at breast height varied with slope aspect, topographic position and elevation, as well as with stand age. Tree size was found to decrease at wind-exposed sites within high-elevation zones.     

Post-fire natural regeneration of a <Emphasis Type="Italic">Pinus pinaster</Emphasis> forest in NW Spain

The aim of this study was to analyse the regeneration of Pinus pinaster after wildfire and the possible inter and intraspecific competition during the first 3 years after fire. The study area is located in a P. pinaster stand in León province (NW Spain). Three study sites (S1, S2 and S3) were established in an area burned in 1998. In each site, three permanent plots (20 × 1 m) were marked. A total of 20 quadrats of 1 m ² were studied in each plot. The number and height of pine seedlings 1, 2 and 3 years after fire was recorded in each quadrat. The regeneration of understorey vegetation in the quadrats was analysed concurrently. The significance of linear correlations among the number and height of seedlings and understorey vegetation cover was tested by calculating Pearson correlation coefficients.Seed germination and seedling emergence took place massively during the first year after the fire and decreased through time. The height growth was constant over the 3 years at site S2, while a growth burst could be observed between years 2 and 3 at sites S1 and S2. Also, pines from site S2 reached shorter maximum heights in all years compared to pines from site S1 and S3. The understorey vegetation showed minimal regeneration during the first year but then increased greatly with time. Woody understorey cover and total vegetation cover were negatively correlated with pine seedling density in sites with a high number of seedlings (e.g. S1 and S3). When woody cover, total cover and pine seedling density were low (e.g. S2), there were no correlations. There was a positive correlation between vegetation cover and the maximum height of Pinus seedlings in all study sites.