兴安落叶松过伐林枯立木分布格局特征分析
Analysis on Distribution Pattern Characteristics of Standing Dead Trees in Larix gmelinii Overcutting Forest
-
摘要: 以内蒙古根河林业局潮查林场境内的在20世纪80年代初主伐利用后形成的兴安落叶松过伐林为研究对象,利用兴安落叶松林8块标准地每木定位数据,分析林木分布格局和样方(5 m×5 m)林木株数对枯立木株数影响,探讨了林分大树和更新幼树位置与枯立木位置的关系,阐明了枯立木分布格局形成机制。结果表明:1)各树种枯立木比例,随树种组成成数增加而增大。枯立木主要在更新幼树阶段形成,径级分布集中在4径阶以下,其株数占总数的比例平均达82.2%。在更新幼树(含枯立木)中,生成枯立木的比例平均达8.8%。2)枯立木分布格局为聚集分布。林木分布格局、样方林木株数和更新株数与枯立木株数有显著正相关关系,林木分布格局对枯立木分布格局无显著影响。林木聚集度越大,形成枯立木的可能性越大,数量也就越多。3)枯立木位置与更新幼树和大树位置有显著相关关系。主要表现为落叶松和白桦相互关系。枯立木出现位置主要在大树和更新幼树集聚区域。大树对枯立木形成影响较更新幼树大,而且均以落叶松较白桦明显。白桦更新幼树对落叶松枯立木的形成,无显著影响。受影响的枯立木主要是枯立木株数中所占比例和树种组成成数较高的树种。影响枯立木位置的林木主要取决于其样方内位置和林木株数。Abstract: The Larix gmelinii overcutting forest formed by final cutting in the 1980s at Chaocha Forest Farm, Genhe Forestry Bureau of Inner Mongolia was investigated. Based on the tree's location data of 8 sample plots in the L. gmelinii forest, the impacts of forest stand pattern and quadrat (5 m×5 m) stem-number on the amount of dead standing trees were analyzed, the relationship between the location of big trees and the regeneration saplings and the location of dead standing trees was discussed, and the forming mechanism of distribution pattern of dead standing trees was clarified. The results are as follows. 1. The ratio of dead standing trees increased with the increase of tree species. The dead standing trees were formed mainly in the stage of regeneration saplings, with the diameter class distribution mainly being below the fourth diameter class, and the average ratio of trees accounting for 82.2% of the total. In the regeneration saplings (including dead standing trees), an average ratio of production of dead standing trees is 8.8%. 2. The distribution of dead standing trees followed a aggregated pattern. The forest stand pattern, the quadrat stem-number and the amount of regeneration trees were in a significant correlation with the amount of dead standing trees. The forest stand pattern had not a significant effect on the pattern of dead standing trees. If the degree of aggregation of the forest is greater, the probability of the formation of dead standing trees will be greater, and the amount will be greater. 3. The location of dead standing trees had a significant correlation with the location of regeneration saplings and regeneration big trees. The main performance was the mutual relation between larch and white birch. The location of dead standing trees was mainly at the aggregation area of the big trees and regeneration saplings. Compared to the regeneration saplings, the big trees had greater impact on the dead standing trees, and specifically, the impact from larch was greater than that from the white birch. The white birch's regeneration saplings had not a significant impact on the formation of larch's dead standing trees. The dead standing trees affected were mainly the species with a higher ratio or greater amount of dead standing trees upon the species of trees. The forest that had an impact on dead standing trees depended mainly on the position of the sample trees and the stem-number.
-
Key words:
- Larix gmelinii
- / overcutting forest
- / standing dead trees
- / distribution pattern
-
[1] 唐旭利,周国逸.南亚热带典型森林演替类型粗死木质残体贮量及其对碳循环的潜在影响[J].植物生态学报, 2005, 29 (4): 559-568. [2] Christopher M, Christoph S, Clare K, et al. Coarse woody debris an the carbon balance of a north temperate forest[J].Forest Ecology and Management, 2007,244(1/3):60-67. [3] Woldendorp G, Keenan R J. Coarse woody debris in Australian forest ecosystems a review[J]. Austral Ecology, 2005,30:834-843. [4] Bigler C, Veblen T. Changes in litter and dead wood loads following tree death beneath subalpine conifer species in northern Colorado[J].Canadian Journal of Forest Research, 2011,41(2):331-340. [5] Beets P N, Hood I A, Kimberley M O, et al. Coarse woody debris decay rates for seven indigenous tree species in the central North Island of New Zealand[J]. Forest Ecology and Management, 2008,256:548-557. [6] 何东进,何小娟,洪 伟,等.森林生态系统粗死木质残体的研究进展[J].林业科学研究,2009,22(5):715-721. [7] Harmon M E, Franklin J F, Swanson F J, et al. Ecology of coarse Wood debris in temperate ecosystems[J]. Advances in Ecological Researches, 1986,15:133-302. [8] Schlegel B C, Donoso P J. Effects of forest type and stand structure on Coarse Woody Debris in old-growth rainforests in the Valdivian Andes, south-central Chile[J].Forest Ecology and Management, 2008,225:1906-1914. [9] Brin A, Meredieu C, Piou D, et al. Changes in quantitative patterns of dead wood in maritime pine plantations over time[J]. Forest Ecology and Management, 2008,256:913-321. [10] Pesonen A, Leino O, Maltamo M, et al. Comparison of field sampling methods for assessing coarse woody debris and use of airborne laser scanning as auxiliary information[J]. Forest Ecology and Management, 2009,257:1532-1541. [11] 何 帆,王得祥,张宋智,等.小陇山林区主要森林群落凋落物及死木质残体储量[J].应用与环境生物学报,2011,17(1):046-050. [12] 王 飞,张秋良,王 冰,等.不同年龄杜香-兴安落叶松林粗木质残体贮量及特征[J].生态学杂志,2012,31(12):2981-2989. [13] 安 云,丁国栋,高广磊,等.华北土石山区天然次生林枯立木数量特征与分布格局[J].水土保持通报,2012,32(4):246-250. [14] 罗大庆,郭泉水,黄 界,等.西藏色季拉原始冷杉林死亡木特征研究[J].生态学报,2004,24(3): 635-639. [15] 金光泽,刘志理,蔡慧颖,等.小兴安岭谷地云冷杉林粗木质残体的研究[J].自然资源学报,2009,24(7):1256-1266. [16] 邓 云,张文富,邓晓保,等.西双版纳热带季节雨林粗木质物残体储量及其空间分布[J].生态学杂志,2012,31(2):261-270. [17] 刘妍妍,金光泽.地形对小兴安岭阔叶红松(Pinus koraiensis)林粗木质残体分布的影响[J].生态学报,2009,29(3):1398-1407. [18] 刘妍妍,金光泽.小兴安岭阔叶红松林粗木质残体基础特征[J].林业科学,2010,46(4):8-14. [19] 刘志华,常 禹,胡远满,等.呼中林区与呼中自然保护区森林粗木质残体储量的比较[J].植物生态学报,2009,33(6):1075-1083. [20] 张秋良,王 飞,李小梅,等.藓类-兴安落叶松林木质物残体贮量及组成[J].生态环境学报,2013,22(3):437-442. [21] Webster C R, Jenkins M A. Coarse woody debris dynamics in the southern Appalachians as affected by topographic position and anthropogenic disturbance history[J].Forest Ecology and Management, 2005,217:319-330. [22] 惠刚盈,Klausvon Gadow, 胡艳波,等.结构化森林经营[M].北京:中国林业出版社,2007:114-120. [23] 韩铭哲.兴安落叶松自然更新格局和种群的生态对策[J].内蒙古林学院学报,1994,1(2):1-10. [24] 玉 宝,乌吉斯古楞,王百田,等.大兴安岭兴安落叶松天然林林隙地被物变化特征研究[J].林业科学研究,2009,22(2):213-218. -

计量
- 文章访问数: 3048
- HTML全文浏览量: 345
- PDF下载量: 834
- 被引次数: 0