Orum Thomas V, Ferguson Nancy, Mihail Jeanne D
Sweetwater Center, Tucson, Arizona, United States of America.
Division of Plant Sciences, University of Missouri, Columbia, Missouri, United States of America.
PLoS One. 2016 Aug 9;11(8):e0160899. doi: 10.1371/journal.pone.0160899. eCollection 2016.
Annual census data spanning seventy-five years document mortality and regeneration in a population of saguaro cactus (Carnegiea gigantea) in the Cactus Forest of the Rincon Mountain District of Saguaro National Park near Tucson, AZ. On 6 four-hectare plots, each saguaro was censused and a methodical search for new saguaros was conducted annually each year from 1942 through 2016, with the exception of 1955. Regeneration has been episodic with 828 plants established from 1959 through 1993 compared with 34 plants established between 1942 and 1958 and only three plants established after 1993. The years preceding 1959 and following 1993, include some of the driest decades in centuries in southern Arizona. While woodcutting and cattle grazing are believed to be among the causes of decades of failed regeneration prior to 1958, neither of these factors contributed to the failed regeneration following 1993. The height structure of the population from 1942 to 2016 shifted dramatically from a population dominated by large saguaros (> 5.4 m tall) in the first three decades of the study to a population dominated by small saguaros (< 1.8 m tall) in the most recent two decades. Mortality is shown to be strongly age dependent. In the year following the 2011 catastrophic freeze, 21 of 59 plants older than 80 years died compared with zero deaths in 270 plants between the ages of 29 and 80 years. Saguaros under 40 years old, growing under small shrubs or in the open, have a lower probability of survival than better protected saguaros. Long-term population monitoring is essential to understanding the complex impacts of human and environmental factors on the population dynamics of long-lived species.
跨越75年的年度普查数据记录了亚利桑那州图森市附近索诺兰国家公园林孔山区仙人掌林里巨人柱仙人掌(Carnegiea gigantea)种群的死亡率和更新情况。在6个4公顷的地块上,对每一株巨人柱进行了普查,并于1942年至2016年(1955年除外)每年对新的巨人柱进行系统搜索。更新情况呈阶段性,1959年至1993年有828株植株更新,而1942年至1958年只有34株,1993年之后仅有3株。1959年之前和1993年之后的年份,包括亚利桑那州南部几个世纪以来最干旱的几十年。虽然伐木和放牧被认为是1958年之前几十年更新失败的原因之一,但这两个因素都不是1993年之后更新失败的原因。1942年至2016年该种群的高度结构发生了巨大变化,从研究的前三十年以大型巨人柱(>5.4米高)为主的种群,转变为最近二十年以小型巨人柱(<1.8米高)为主的种群。死亡率显示出强烈的年龄依赖性。在2011年灾难性霜冻后的一年里,59株年龄超过80岁的植株中有21株死亡,而270株年龄在29岁至80岁之间的植株无一死亡。40岁以下的巨人柱,生长在小灌木下或空旷处,其存活概率低于受到更好保护的巨人柱。长期的种群监测对于理解人类和环境因素对长寿物种种群动态的复杂影响至关重要。