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1.
冯璐  卜兆君  李振新  冯亚敏 《生态学报》2015,35(9):2993-2997
长寿有性繁殖体对于植物种群的长存具有重要意义,迄今,泥炭地苔藓植物孢子长寿性研究还很少。在长白山哈泥泥炭地钻取丘间表层泥炭样品,测定泥炭腐殖化度和烧失量,逐层提取和培养泥炭藓孢子,研究埋藏时间对孢子萌发的影响。结果表明,丘间泥炭藓孢子埋藏环境中,随着埋深的增加即埋藏年限的增加,泥炭腐殖化度和烧失量总体上分别呈现增加和递减的趋势,而地层泥炭藓孢子萌发率呈现直线递减的规律,但在埋藏近150余年后孢子萌发率仍可达40%。研究进一步证明泥炭藓具有长期持久孢子库,根据推算,泥炭地丘间埋藏环境中,泥炭藓孢子最大寿命可超过400a。  相似文献   

2.
研究泥炭地特征性环境因子——淹水、少氧和化感物质对泥炭藓孢子持久性的影响, 可深入理解泥炭地泥炭藓持久孢子库的形成机制, 为退化泥炭地泥炭藓地被恢复研究提供参考。该研究以藓丘种和丘间种两种泥炭藓的孢子为试验材料, 通过室内模拟控制实验的方法, 研究泥炭藓孢子在空气、超纯水、泥炭地地表水和泥炭藓沥出液中, 及3种速率充气下, 孢子萌发力持久性的变化。经充气处理后, 泥炭藓孢子持久性显著低于不充气处理。不充气时, 泥炭藓孢子在含有化感物质的泥炭地地表水和泥炭藓沥出液中保存, 持久性显著高于在超纯水中保存。通径分析结果显示, 溶解氧是影响泥炭地泥炭藓孢子持久性的主要因子和限制因子, 养分元素氮(TN)和磷(TP)的浓度为孢子持久性的负作用因子。研究结果表明, 泥炭藓孢子散布于苔藓地被基质或淹水的丘间生境中, 比暴露于空气或在无化感物质的水中, 能更好地维持萌发力。泥炭地中, 泥炭藓孢子和其他植物的繁殖体的超长寿命可能归因于少氧、养分贫乏和丰富的化感物质等泥炭地特征性环境因子。  相似文献   

3.
研究泥炭地特征性环境因子——淹水、少氧和化感物质对泥炭藓孢子持久性的影响,可深入理解泥炭地泥炭藓持久孢子库的形成机制,为退化泥炭地泥炭藓地被恢复研究提供参考。该研究以藓丘种和丘间种两种泥炭藓的孢子为试验材料,通过室内模拟控制实验的方法,研究泥炭藓孢子在空气、超纯水、泥炭地地表水和泥炭藓沥出液中,及3种速率充气下,孢子萌发力持久性的变化。经充气处理后,泥炭藓孢子持久性显著低于不充气处理。不充气时,泥炭藓孢子在含有化感物质的泥炭地地表水和泥炭藓沥出液中保存,持久性显著高于在超纯水中保存。通径分析结果显示,溶解氧是影响泥炭地泥炭藓孢子持久性的主要因子和限制因子,养分元素氮(TN)和磷(TP)的浓度为孢子持久性的负作用因子。研究结果表明,泥炭藓孢子散布于苔藓地被基质或淹水的丘间生境中,比暴露于空气或在无化感物质的水中,能更好地维持萌发力。泥炭地中,泥炭藓孢子和其他植物的繁殖体的超长寿命可能归因于少氧、养分贫乏和丰富的化感物质等泥炭地特征性环境因子。  相似文献   

4.
作为生态系统稳定性维持的一个重要因素,火对泥炭地优势植物泥炭藓(Sphagnum)孢子库的影响尚不清楚.以采自长白山区泥炭地的泥炭土和3种泥炭藓的成熟孢子为实验材料,室内模拟火烧,以此设置不同温度水平(20、40、60或100℃,持续0.5、1、2、4或10 min),对泥炭藓孢子进行热激处理,经萌发实验后,研究火烧高温对孢子萌发率的影响.结果显示,火烧期间各层土温随深度而递减,表层泥炭可达300℃的极端高温,而1 cm深温度仅为70℃,体现出泥炭土良好的热缓冲性;40℃的热激可使锈色泥炭藓(S.fuscum)与中位泥炭藓(S.magellanicum)孢子萌发率提高20%与50%;60℃的热激使尖叶泥炭藓(S.capillifolium)孢子的萌发率提高1倍;100℃热激对3种泥炭藓孢子萌发则有强烈的抑制作用.研究表明,泥炭藓孢子耐受高温的能力有限,但土壤中的孢子凭借泥炭的良好热缓冲性,可以躲避火烧高温造成的致命伤害,适度的热激甚至能提高其萌发力,对其在火后的建植及种群的长存可能有重要意义.  相似文献   

5.
适量的烟气能够促进有性繁殖体萌发,但迄今尚无辅助烟气处理探究孢子生活力快速检测方法的研究报道。该文选择毛缘泥炭藓(Sphagnum fimbriatum)、中位泥炭藓(S.magellanicum)和粗叶泥炭藓(S.squarrosum)作为材料,分别使用亚甲基蓝染色法、四唑(TTC)染色法、碘-碘化钾(I2-KI)染色法和红墨水染色法对泥炭藓孢子进行染色,并比照营养液、烟溶液+营养液培养的孢子萌发试验,对比研究泥炭地苔藓植物孢子生活力快速检测的最佳方法。结果表明:亚甲基蓝染色法的染色效果最为明显,TTC和I2-KI均未能使泥炭藓孢子着色,孢子对红墨水虽有着色反应但不清晰;与营养液培养相比,添加烟溶液使毛缘泥炭藓、中位泥炭藓和粗叶泥炭藓孢子萌发率分别提高5%、5%和18%;使用亚甲基蓝染色的孢子染色率与经烟溶液处理过的孢子萌发率最为接近。综上认为,亚甲基蓝染色法能快速检测泥炭藓孢子的生活力。  相似文献   

6.
有性繁殖体库对于植物种群的长存具有重要意义,迄今为止,泥炭地尚无苔藓植物长期的持久孢子库的直接实验证据。在长白山哈泥泥炭地,钻取50 cm表层泥炭样品,运用落叶松测年法推算泥炭地地层泥炭藓孢子的埋藏时间,经逐层提取和培养尖叶泥炭藓孢子,研究埋藏时间对孢子萌发率的影响。结果表明,随着埋藏时间的增加,尖叶泥炭藓孢子萌发率呈现对数函数递减的趋势。研究获得泥炭地苔藓植物具有长期的持久孢子库的实验证据,即埋藏112年的尖叶泥炭藓孢子仍具萌发潜力。据推算,泥炭藓孢子最大寿命可达396.4年。  相似文献   

7.
作为优势植物, 泥炭藓(Sphagnum)在泥炭沼泽中缺乏有性更新的原因尚不清楚。针对影响孢子萌发的光强和养分条件, 以泥炭藓(S. palustre)为材料, 通过室内孢子萌发实验, 研究不同光强和养分浓度对孢子萌发率、萌发势及萌发指数的影响。4 种培养基中, 养分浓度高的营养液培养基中孢子萌发率最高, 达到60%, 其次为养分浓度与营养液相近的琼脂+营养液培养基, 萌发率为48%, 再次为养分水平很低的沼泽水培养基, 萌发率约为30%, 几乎无养分的蒸馏水培养基中萌发率最低, 约为5%。萌发势和萌发指数亦呈现相同的规律。琼脂+营养液和营养液培养基较沼泽水和蒸馏水培养基孢子萌发时间提前约3 天时间。增加光强使孢子萌发率仅提高10%。研究表明, 低养分浓度和弱光照均不利于孢子萌发, 相对而言, 泥炭沼泽的贫营养特征应是限制泥炭藓有性更新的更重要因素。  相似文献   

8.
适量烟气能促进种子萌发,但对苔藓植物孢子的作用尚不清楚.选取采自长白山区泥炭地的粗叶泥炭藓和中位泥炭藓的孢蒴为试验材料,通过燃烧泥炭地植物产生烟气,制备烟溶液,分别与不同大小(大:直径为2.10~2.50 mm;小:直径为1.50~1.90 mm)以及不同保存时长(旧:4.3和6.3年;新:0.3年)的孢蒴进行两组双因素试验,经不同时长的烟溶液浸泡和萌发试验,模拟研究烟气、孢蒴大小和保存时长对苔藓植物孢子萌发的影响.结果表明: 烟溶液浸泡影响孢子萌发,培养10 d时,不同时长的烟溶液浸泡均可使孢子的萌发率提高5倍以上,小孢蒴孢子的萌发率高;培养21 d时,仅适度浸泡(3 d)表现出促进萌发的作用,孢蒴大小对孢子萌发率无影响;烟溶液浸泡对长时间保存(4.3和6.3年)的孢蒴孢子萌发无促进作用.研究表明,适量烟气可加速新泥炭藓孢子以及小孢蒴孢子的萌发.在存在不定期火烧干扰的泥炭地中,与对种子植物的作用类似,烟气可能在苔藓植物种群的有性更新和种群维持中发挥重要作用.  相似文献   

9.
泥炭藓是北方泥炭地的优势植物,其高光谱特征研究很少。本研究采用高光谱遥感技术,对不同水位埋深条件下(藓丘及丘间)生长的相同种类泥炭藓植物,及同一水位埋深条件下的不同种类泥炭藓植物的光谱特征进行研究。结果表明,不同种类泥炭藓属植物的光谱反射特征具有明显种间差异,主要反映在绿峰、红边的差异上。由于水分条件差异,生长在高丘和低丘的锈色泥炭藓、泥炭藓及中位泥炭藓在可见光和近红外波段的光谱反射率均具有显著差异,高丘的泥炭藓属植物的反射率均高于低丘的泥炭藓属植物。本研究所获得的东北地区哈泥泥炭地几种泥炭藓属植物的详细光谱信息,可以为高分辨率航空影像和卫片解译泥炭藓湿地提供地面基础。  相似文献   

10.
泥炭藓及其孢子萌发和有性生殖   总被引:10,自引:0,他引:10  
包文美  曹建国 《生物学通报》2001,36(1):8-9,F003
将泥炭藓孢子萌发为配子体和有性生殖及精子形态等细节,用作者拍摄的活体照片,介绍给读者,以期对植物教学有所补充。  相似文献   

11.
泥炭藓(Sphagnum)是湿地土壤碳的重要来源, 在土壤碳累积过程中发挥着关键作用, 但有关亚热带湿地泥炭藓生长与分解的研究鲜有报道。该研究选择鄂西南亚高山泥炭藓湿地为研究区域, 原位开展不同微生境泥炭藓的生长及其凋落物的分解实验, 室内测试凋落物的化学成分, 探讨亚热带亚高山湿地泥炭藓的生长与分解规律。结果表明: 泥炭藓在自然状态生长12个月后, 丘上和丘间两种微生境下泥炭藓的平均高度增长量分别为2.9和2.7 cm, 对应的净生产量分别为270.94和370.88 g·m -2, 生长时间与微生境对泥炭藓的高度增长量及净生产量均有显著影响, 且两者之间存在交互作用, 但是两种微生境下泥炭藓的生长变化过程不同; 两种微生境下泥炭藓的平均生长速率(2017年7-10月)为0.33 mm·d -1, 其生长速率高于寒温带地区。另外, 分解时间对泥炭藓的分解量有显著影响, 其残留率随时间增加表现为先减少后增加的趋势。12个月后, 丘间、丘上和水坑3种微生境下最终残留率分别为100.67%、90.54%和85.63%。凋落物中碳含量、碳氮比和多酚含量相比初始值均有所下降, 氮含量则为增加。同时, 微生境对凋落物分解的影响取决于分解时间。分解3个月时, 微生境之间凋落物的分解量差异显著, 其他时间段差异不明显。  相似文献   

12.
高谦  曹同 《植物研究》1984,4(4):129-136
泥炭藓(Sphagnum)是水湿或沼泽地区丛生藓类。其植物体形态和构造分化简单,孢子体仅具由配子体组织发育的假蒴柄;孢蒴球形,盖裂,无蒴轴及蒴齿分化,因而为鲜纲中一个独立的亚纲,在苔藓系统排列中,列为原始的类型之一。  相似文献   

13.
Bond-Lamberty B  Gower ST 《Oecologia》2007,151(4):584-592
Bryophytes dominate the carbon and nitrogen cycling of many poorly drained terrestrial ecosystems and are important in the vegetation-atmosphere exchange of carbon and water, yet few studies have estimated their leaf area at the stand scale. This study quantified the bryophyte-specific leaf area (SLA) and leaf area index (LAI) in a group of different-aged boreal forest stands in well and poorly drained soils. Species-specific SLA (for three feather mosses, four Sphagnum spp. and Aulacomnium palustre mixed with Tomentypnum nitens) was assessed by determining the projected area using a flatbed scanner and cross-sectional geometry using a dissecting microscope. The hemisurface leaf area was computed as the product of SLA and live biomass and was scaled by coverage data collected at all stands. Pleurozium schreberi dominated the spatial coverage, biomass and leaf area in the well-drained stands, particularly the oldest, while S. fuscum and A. palustre were important in the poorly drained stands. Live moss biomass ranged from 47 to 230 g m−2 in the well-drained stands dominated by feather mosses and from 102 to 228 g m−2 in the poorly drained stands. Bryophyte SLA varied between 135 and 473 cm2 g−1, for A. palustre and S. capillifolium, respectively. SLA was strongly and significantly affected by bryophyte species, but did not vary between stands; in general, there was no significant difference between the SLA of non-Sphagnum mosses. Bryophyte LAI increased with stand age, peaking at 3.1 and 3.7 in the well and poorly drained stands, respectively; this represented approximately 40% of the overstory LAI in the well-drained stands and 100–1,000% in the poorly drained stands, underscoring the important role bryophytes play in the water and carbon budgets of these boreal forests.  相似文献   

14.
This study examined the nitrogen (N) dynamics of a black spruce (Picea mariana (Mill.) BSP)-dominated chronosequence in Manitoba, Canada. The seven sites studied each contained separate well- and poorly drained stands, originated from stand-killing wildfires, and were between 3 and 151 years old. Our goals were to (i) measure total N concentration ([N]) of all biomass components and major soil horizons; (ii) compare N content and select vegetation N cycle processes among the stands; and (iii) examine relationships between ecosystem C and N cycling for these stands. Vegetation [N] varied significantly by tissue type, species, soil drainage, and stand age; woody debris [N] increased with decay state and decreased with debris size. Soil [N] declined with horizon depth but did not vary with stand age. Total (live + dead) biomass N content ranged from 18.4 to 99.7 g N m−2 in the well-drained stands and 37.8–154.6 g N m−2 in the poorly drained stands. Mean soil N content (380.6 g N m−2) was unaffected by stand age. Annual vegetation N requirement (5.9 and 8.4 g N m−2 yr−1 in the middle-aged well- and poorly drained stands, respectively) was dominated by trees and fine roots in the well-drained stands, and bryophytes in the poorly drained stands. Fraction N retranslocated was significantly higher in deciduous than evergreen tree species, and in older than younger stands. Nitrogen use efficiency (NUE) was significantly lower in bryophytes than in trees, and in deciduous than in evergreen trees. Tree NUE increased with stand age, but overall stand NUE was roughly constant (∼ ∼150 g g−1 N) across the entire chronosequence.  相似文献   

15.
Artificial drainage (ditching) is widely used to increase timber yield in northern forests. When the drainage systems are maintained, their environmental impacts are likely to accumulate over time and along accompanying management, notably after logging when new forest develops on decayed peat. Our study provides the first comprehensive documentation of long-term ditching impacts on terrestrial and arboreal biodiversity by comparing natural alder swamps and second-generation drained forests that have evolved from such swamps in Estonia. We explored species composition of four potentially drainage-sensitive taxonomic groups (vascular plants, bryophytes, lichens, and snails), abundance of species of conservation concern, and their relationships with stand structure in two-ha plots representing four management types (ranging from old growth to clearcut). We found that drainage affected plot-scale species richness only weakly but it profoundly changed assemblage composition. Bryophytes and lichens were the taxonomic groups that were most sensitive both to drainage and timber-harvesting; in closed stands they responded to changed microhabitat structure, notably impoverished tree diversity and dead-wood supply. As a result, natural old-growth plots were the most species-rich and hosted several specific species of conservation concern. Because the most influential structural changes are slow, drainage impacts may be long hidden. The results also indicated that even very old drained stands do not provide quality habitats for old-growth species of drier forest types. However, drained forests hosted many threatened species that were less site type specific, including early-successional vascular plants and snails on clearcuts and retention cuts, and bryophytes and lichens of successional and old forests. We conclude that three types of specific science-based management tools are needed to mitigate ditching effects on forest biodiversity: (i) silvicultural techniques to maintain stand structural complexity; (ii) context-dependent spatial analysis and planning of drained landscapes; and (iii) lists of focal species to monitor and guide ditching practices.  相似文献   

16.
Natural peatlands accumulate carbon (C) and nitrogen (N). They affect the global climate by binding carbon dioxide (CO2) and releasing methane (CH4) to the atmosphere; in contrast fluxes of nitrous oxide (N2O) in natural peatlands are insignificant. Changes in drainage associated with forestry alter these greenhouse gas (GHG) fluxes and thus the radiative forcing (RF) of peatlands. In this paper, changes in peat and tree stand C stores, GHG fluxes and the consequent RF of Finnish undisturbed and forestry‐drained peatlands are estimated for 1900–2100. The C store in peat is estimated at 5.5 Pg in 1950. The rate of C sequestration into peat has increased from 2.2 Tg a‐‐1 in 1900, when all peatlands were undrained, to 3.6 Tg a‐‐1 at present, when c. 60% of peatlands have been drained for forestry. The C store in tree stands has increased from 60 to 170 Tg during the 20th century. Methane emissions have decreased from an estimated 1.0–0.5 Tg CH4‐‐C a‐‐1, while those of N2O have increased from 0.0003 to 0.005 Tg N2O‐‐N a‐‐1. The altered exchange rates of GHG gases since 1900 have decreased the RF of peatlands in Finland by about 3 mW m‐‐2 from the predrainage situation. This result contradicts the common hypothesis that drainage results in increased C emissions and therefore increased RF of peatlands. The negative radiative forcing due to drainage is caused by increases in CO2 sequestration in peat (‐‐0.5 mW m‐‐2), tree stands and wood products (‐‐0.8 mW m‐‐2), decreases in CH4 emissions from peat to the atmosphere (‐‐1.6 mW m‐‐2), and only a small increase in N2O emissions (+0.1 mW m‐‐2). Although the calculations presented include many uncertainties, the above results are considered qualitatively reliable and may be expected to be valid also for Scandinavian countries and Russia, where most forestry‐drained peatlands occur outside Finland.  相似文献   

17.
The analysis of the micromycete complexes of oligotrophic peat deposits in the Vasyugan Marsh by direct count and culture methods showed that micromycete carbon comprises no more than 3% of the total peat carbon and that the microscopic fungal biomass varies from 2 to 13 tons/hectare, depending on the season and the peat deposit thickness. Fungal spores were found in all layers of the peat deposits, whereas the mycelium was found only in the active peat layer. The high abundance of eukaryotic cells in the peats was due to the presence of yeastlike cells rather than fungal spores. Analyses by culture methods showed that micromycetes were present in all peat layers and that their abundance tended to decrease with depth, except for yeasts, which were uniformly distributed in a vertical direction. The micromycete complexes of the peat deposits were similar in their diversity and abundance of dominant species but differed in the composition of minor species. Peat yeasts were dominated by ascomycetes.  相似文献   

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