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Clonal regeneration of an arrow bamboo, Fargesia qinlingensis, following giant panda herbivory

机译:大熊猫食草后箭竹秦岭箭竹的克隆再生

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Characteristics of giant panda herbivory sites and clonal regeneration of an arrow bamboo Fargesia qinlingensis following giant panda grazing were studied in the Qinling Mountains of China. Three types of plots were located in a pandas’ summer habitat in 2002: herbivory (naturally grazed by giant pandas), clipped (simulated panda herbivory), and control. Average area of herbivory sites was 2.92 m2 and average distance from herbivory sites to the closest tree (dbh > 10 cm) was 1.0 m. Pandas avoided thin bamboo culms with basal diameters <5 mm. Average height of stumps of culms grazed by panda was 0.67 m and average density of grazed culms was 9.0 culms m?2. Annual culm mortality rate was significantly greater in herbivory and clipped plots than in control plots while annual recruitment rate was not significantly different among the three plot types in 2003. Neither recruitment rate nor mortality rate were significantly different among the three plot types in 2004. Annual recruitment rate was significantly greater than annual mortality rate only in control plots in both 2003 and 2004, suggesting static ramet dynamics in disturbed plots (herbivory and clipped). Density of new shoots was not significantly different, but basal diameter of new shoots was significantly less in herbivory plots compared to control plots in 2002. Differences of annual mortality rate and growth of new shoots found between control plots and herbivory plots suggest that clonal regeneration of F. qinlingensis culms was negatively affected by giant panda grazing. Therefore, no evidence of a clonal integration compensatory response to panda herbivory was found in F. qinlingensis.
机译:研究了中国秦岭大熊猫放牧后大箭竹食草位点的特征和秦岭箭竹的克隆再生。 2002年,大熊猫的夏季栖息地位于三种类型的地块:草食性(大熊猫自然放牧),修剪(模拟的熊猫食性)和控制。草食场所的平均面积为2.92 m2 ,食草场所到最近的树木(dbh> 10 cm)的平均距离为1.0 m。熊猫避免使用直径小于5毫米的细竹杆。熊猫放牧的茎秆的平均树高为0.67 m,草食的茎秆的平均密度为9.0 culm?2 。食草和修剪地块的年度茎秆死亡率显着高于对照地块,而2003年这三种地块的年招聘率没有显着差异。2004年这三种地块的招聘率和死亡率均无显着差异。仅在2003年和2004年的对照地块中,招募率显着高于年死亡率,这表明受干扰地块(草食和修剪)的静态分株动态。与2002年的对照样地相比,食草样地新芽的密度没有显着差异,但是新芽的基径显着减小。对照样地和食草样地之间发现的年死亡率和新芽的生长差异表明,克隆的再生大熊猫放牧对秦岭镰刀菌有不利影响。因此,在秦岭草中没有发现对熊猫食草性克隆整合补偿反应的证据。

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