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Population viability analysis and fire return intervals for an endemic Florida scrub mint.

机译:佛罗里达特有灌木灌木薄荷的种群生存力分析和回火间隔。

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We use population viability analysis of an endangered Florida scrub mint (USA), Dicerandra frutescens, to specify the optimal fire return intervals for its long-term persistence and for its specific habitat. We derived 83 population projection matrices from 13 years of demographic data from eight populations, 59 matrices from scrub populations and 24 from firelane or yard edges. Seed dormancy and germination transitions were inferred based on experimental data and verified by comparing modelled vs. observed population trajectories. Finite rates of increase in scrub sites were highest shortly after fire and declined steeply through 10 years postfire. The break-even value of lambda =1 was passed quickly, in approximately six years, suggesting that populations >6 years postfire were already facing decline. The decline was probably related to the rapid growth of competing shrubs in the habitat of D. frutescens. In long-unburned sites, finite rates of increase were nearly always <1 and declined the most in the long-unburned site with no foot trails or treefall gaps. Finite rates of increase in firelane populations also declined with years since fire or last discing. The yard edge population showed lambda values both >1 and <1, with no temporal trend. Stochastic simulations in scrub sites suggested an optimal regular fire return interval of about 6-12 years. Regular fires at this interval were more favorable than stochastic fire regimes, but stochasticity reduced extinction percentages at longer fire return intervals. Stochastic fire return intervals implied a wider optimal fire return interval of 6-21 years. We suggest that prescribed fire in Florida scrub on yellow sand has occurred (and needs to occur) more frequently than previously recommended..
机译:我们使用濒临灭绝的佛罗里达灌木薄荷(Dicerandra frutescens)的种群生存力分析,为其长期持久性和特定生境指定最佳回火间隔。我们从8个种群的13年人口数据中得出了83个种群投影矩阵,从灌木种群中获得了59个矩阵,从火场或院子边缘获得了24个。根据实验数据推断种子的休眠和发芽转变,并通过比较模拟的种群轨迹和观察的种群轨迹进行验证。火灾发生后不久,灌木场的有限增加率最高,并且在火灾后10年急剧下降。 lambda = 1的收支平衡值很快就通过了,大约在六年内,这表明火灾后> 6年的人口已经面临下降。下降的原因可能与D. frutescens栖息地中竞争性灌木的快速生长有关。在长期未燃烧的地点中,有限的增长率几乎总是<1,并且在长时间未燃烧的地点中没有脚步痕迹或没有树状空隙的情况下下降幅度最大。自从大火或最后一次燃烧以来,火道人口的有限增加率也随着下降而下降。围场边缘种群的λ值均大于1和小于1,没有时间趋势。在灌丛场地的随机模拟表明,最佳的定期回火间隔约为6-12年。在此时间间隔内,定期火灾比随机火灾情况更有利,但在较长的回火间隔内,随机性降低了灭绝百分比。随机回火间隔意味着6-21年的最佳回火间隔。我们建议佛罗里达州规定的大火在黄砂上的擦洗比以前建议的要频繁发生(并且需要发生)。

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