生态学报
生態學報
생태학보
ACTA ECOLOGICA SINICA
2009年
12期
6615-6621
,共7页
李媛良%汪思龙%宿秀江%张伟东%颜绍馗
李媛良%汪思龍%宿秀江%張偉東%顏紹馗
리원량%왕사룡%숙수강%장위동%안소규
单优%林下植被%天然林重建%竹子%亚热带
單優%林下植被%天然林重建%竹子%亞熱帶
단우%림하식피%천연림중건%죽자%아열대
monodominance%understory%reestablishment of natural forest%bamboo%subtropical region
利用1996年在湖南省会同林区布置的20个1 hm~2的实验样地,以剔除或林下不含箬叶竹样地作为对照(C),保留箬叶竹作为处理(I),评估了天然林重建过程中林下单优箬叶竹灌丛形成对树种更新过程的影响.处理10a以后结果显示,箬叶竹灌丛盖度上升到95%.进一步通过2007年两种样地乔木多度、多样性、生物量以及物种组成等指标的测量表明,单优箬叶竹灌丛显著抑制了树种的存活与生长,18~390 cm高度级别的树种多度和多样性显著降低,尽管高度18 cm以下级别的幼苗以及成年树的多度和多样性没有显著下降,但是生物量从幼苗到成年树,处理样地普遍下降.幼苗、幼树、成年树地上部分生物量分别下降47.45%、39.87%、59.64%,地下部分生物量分别下降55.70%、46.08%、63.62%.NMS(非计量多元尺度法)排序进一步表明两种样地具有显著不同的树种组成,揭示两种样地处于不同的演替更新阶段.结果表明单优箬叶竹灌丛的形成能延缓树种更新的进程,因此天然林重建过程中应注意避免该类林下植被的出现.
利用1996年在湖南省會同林區佈置的20箇1 hm~2的實驗樣地,以剔除或林下不含箬葉竹樣地作為對照(C),保留箬葉竹作為處理(I),評估瞭天然林重建過程中林下單優箬葉竹灌叢形成對樹種更新過程的影響.處理10a以後結果顯示,箬葉竹灌叢蓋度上升到95%.進一步通過2007年兩種樣地喬木多度、多樣性、生物量以及物種組成等指標的測量錶明,單優箬葉竹灌叢顯著抑製瞭樹種的存活與生長,18~390 cm高度級彆的樹種多度和多樣性顯著降低,儘管高度18 cm以下級彆的幼苗以及成年樹的多度和多樣性沒有顯著下降,但是生物量從幼苗到成年樹,處理樣地普遍下降.幼苗、幼樹、成年樹地上部分生物量分彆下降47.45%、39.87%、59.64%,地下部分生物量分彆下降55.70%、46.08%、63.62%.NMS(非計量多元呎度法)排序進一步錶明兩種樣地具有顯著不同的樹種組成,揭示兩種樣地處于不同的縯替更新階段.結果錶明單優箬葉竹灌叢的形成能延緩樹種更新的進程,因此天然林重建過程中應註意避免該類林下植被的齣現.
이용1996년재호남성회동림구포치적20개1 hm~2적실험양지,이척제혹림하불함약협죽양지작위대조(C),보류약협죽작위처리(I),평고료천연림중건과정중림하단우약협죽관총형성대수충경신과정적영향.처리10a이후결과현시,약협죽관총개도상승도95%.진일보통과2007년량충양지교목다도、다양성、생물량이급물충조성등지표적측량표명,단우약협죽관총현저억제료수충적존활여생장,18~390 cm고도급별적수충다도화다양성현저강저,진관고도18 cm이하급별적유묘이급성년수적다도화다양성몰유현저하강,단시생물량종유묘도성년수,처리양지보편하강.유묘、유수、성년수지상부분생물량분별하강47.45%、39.87%、59.64%,지하부분생물량분별하강55.70%、46.08%、63.62%.NMS(비계량다원척도법)배서진일보표명량충양지구유현저불동적수충조성,게시량충양지처우불동적연체경신계단.결과표명단우약협죽관총적형성능연완수충경신적진정,인차천연림중건과정중응주의피면해류림하식피적출현.
We evaluated the influence of long-auricled indocalamus (Indocalamus longiauritus Hand.-Mazz.) monodominant thickets in understory layers of tree regenerations during the reestablishment process of natural forests. A manipulative field experiment was performed in pure Chinese fir (Cunninghamia lanceolata (Lamb.) Hook) plantations in Huitong, Hunan Province, located in the subtropical part of China. Ten 1hm~2 permanent plots with long-auricled indocalamus in understory (I) were selected as treatment and another ten 1hm~2 permanent plots (C) were used as control plots in which there is no any bamboo. In 1996, all canopy Chinese fir individuals were removed to improve understory light condition and to promote the establishment of monodominant thickets in these plots. After 10 years, dense bamboo layers with about 95% cover were successfully established. In 2007, we measured the abundance, diversity and biomass of tree seedling, sapling and adult tree by height class in all treatment and control plots. The formation of long-auricled indocalamus monodominant thickets significantly impeded the tree survival and growth. The abundance and diversity of saplings in the 18-390 cm height classes were lower in the treatment plots. Although the dense bamboo layers did not significantly reduce the abundance and diversity of tree seedlings of less than 18 cm height and canopy trees, the biomass of seedlings, saplings and canopy trees decreased by 47.45%, 39.87% and 59.64% for the aboveground portion and by 55.70%, 46.08% and 63.62% for the belowground portion, respectively. Non-metric multidimensional scaling (NMS) ordination showed different patterns in species compositions between treatment and control plots, which further indicated that tree regeneration in these two types of plots was not in the same succession phase. Our results support the hypothesis that the formation of dense bamboo thickets would slow the tree regeneration process. Our study suggests that the formation of monodominant understory layers during reestablishment of natural forest should be avoided.