Hendrickson J R, Briske D D
Department of Rangeland Ecology and Management, Texas A&M University, College Station, TX 77843-2126, USA Fax: (409) 845-6430; e-mail:
Oecologia. 1997 May;110(4):584-591. doi: 10.1007/s004420050199.
The occurrence, longevity, and contribution of axillary bud banks to population maintenance were investigated in a late-seral perennial grass, Bouteloua curtipendula, and a mid-seral perennial grass, Hilaria belangeri, in a semiarid oak-juniper savanna. Axillary buds of both species were evaluated over a 2-year period in communities with contrasting histories of grazing by domestic herbivores. A double staining procedure utilizing triphenyl tetrazolium chloride and Evan's blue indicated that both viable and dormant axillary buds remained attached to the base of reproductive parental tillers for 18-24 months which exceeded parental tiller longevity by approximately 12 months. Bud longevity of the late-seral species, B. curtipendula, exceeded bud longevity of the mid-seral species, H. belangeri, by approximately 6 months. Younger buds located on the distal portion of the tiller base were 3.2 and 1.4 times more likely to grow out than older proximal buds of B. curtipendula and H. belangeri, respectively. The percentage of older proximal buds, which included comparable portions of viable and dormant buds, that grew out to produce tillers following mortality of parental tillers was 6.0% for B. curtipendula and 8.4% for H. belangeri. In spite of the occurrence of relative large axillary bud banks for both species, the magnitude of proximal bud growth did not appear sufficient to maintain viable tiller populations. We found no evidence to support the hypothesis of compensatory bud growth on an individual tiller basis for either species. Grazing history of the communities from which the buds were collected did not substantially affect the number, status, longevity, or outgrowth of axillary buds on an individual tiller basis for either species. However, long-term grazing by domestic herbivores influenced axillary bud availability by modifying population structure of these two species. Bud number per square meter for B. curtipendula was 25% lower in the long-term grazed compared to the long-term ungrazed community based on a reduction in both tiller number per plant and plant number per square meter. In contrast, bud number per square meter for H. belangeri was 190% greater in the long-term grazed than in the long-term ungrazed community based on a large increase in plant density per square meter. Minimal contributions of axillary bud banks to annual maintenance of tiller populations in this mid- and late-seral species underscores the ecological importance of consistent tiller recruitment from recently developed axillary buds. Consistent tiller recruitment in grasslands and savannas characterized by intensive grazing and periodic drought implies that (1) bud differentiation and maturation must be remarkably tolerant of adverse environmental conditions and/or (2) tiller recruitment may resume from buds that mature following the cessation of severe drought and/or grazing, rather than from mature buds that survive these disturbances. These scenarios warrant additional research emphasis given the critical importance of this demographic process to tiller replacement in species populations and the maintenance of relative species abundance in grasslands and savannas.
在半干旱的橡木 - 杜松稀树草原中,对一种演替后期的多年生草本植物弯叶布第罗草(Bouteloua curtipendula)和一种演替中期的多年生草本植物贝氏希拉草(Hilaria belangeri)的腋芽库的发生、寿命以及对种群维持的贡献进行了研究。在有不同家畜放牧历史的群落中,对这两个物种的腋芽进行了为期两年的评估。一种利用氯化三苯基四氮唑和伊文思蓝的双重染色程序表明,有活力和休眠的腋芽在生殖亲本分蘖的基部附着18 - 24个月,这比亲本分蘖的寿命长约12个月。演替后期物种弯叶布第罗草的芽寿命比演替中期物种贝氏希拉草的芽寿命长约6个月。位于分蘖基部远端的较幼芽长出的可能性分别是弯叶布第罗草和贝氏希拉草较老近端芽的3.2倍和1.4倍。亲本分蘖死亡后,包括相当比例有活力和休眠芽的较老近端芽长出形成分蘖的比例,弯叶布第罗草为6.0%,贝氏希拉草为8.4%。尽管这两个物种都存在相对较大的腋芽库,但近端芽生长的规模似乎不足以维持有活力的分蘖种群。我们没有找到证据支持这两个物种中单个分蘖上补偿性芽生长的假设。采集芽的群落的放牧历史对于这两个物种中单个分蘖上的腋芽数量、状态、寿命或长出情况没有实质性影响。然而,家畜的长期放牧通过改变这两个物种的种群结构影响了腋芽的可用性。基于每株分蘖数量和每平方米植株数量的减少,长期放牧的群落中弯叶布第罗草每平方米的芽数量比长期未放牧的群落低25%。相比之下,基于每平方米植株密度的大幅增加,长期放牧的群落中贝氏希拉草每平方米的芽数量比长期未放牧的群落高190%。在这种演替中期和后期物种中,腋芽库对分蘖种群年度维持的贡献极小,这突出了从最近发育的腋芽持续招募分蘖的生态重要性。在以高强度放牧和周期性干旱为特征的草原和稀树草原中,持续的分蘖招募意味着:(1)芽的分化和成熟必须对不利环境条件具有显著的耐受性,和/或(2)分蘖招募可能从严重干旱和/或放牧停止后成熟的芽恢复,而不是从在这些干扰中存活的成熟芽恢复。鉴于这一人口统计学过程对物种种群中分蘖替代以及草原和稀树草原中相对物种丰度维持的至关重要性,这些情况值得进一步的研究关注。