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Patterns of herbivory-induced mortality of a dominant non-native tree/shrub (Tamarix spp.) in a southwestern US watershed

机译:食草动物导致的美国西南流域主要非本地树/灌木(Tamarix spp。)死亡的模式

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The capacity for plant species or populations to cope with herbivory depends in large part on the complex interactions between resource availability, life history and adaptive strategies to maximize defense and/or tolerance to herbivory. Given these complex interactions, the impacts of repeated herbivory on plant stress and subsequent mortality is often difficult to predict. To better understand relationships between herbivory and environmental condition, we studied the relationship between the non-native shrub/tree tamarisk (Tamarix spp.) and a specialist herbivore, the northern tamarisk leaf beetle (Diorhabda carinulata) released as a biological control agent of Tamarix in the Virgin River watershed in the southwestern United States. The beetle feeds exclusively on Tamarix foliage resulting in complete stand foliage desiccation (i.e. defoliation) that lasts several weeks. Approximately 900 Tamarix plants were surveyed over three consecutive growing seasons for canopy dieback and mortality across 10 sites varying in the number of defoliation events, tree height, soil salinity, soil texture and bulk leaf carbon isotope ratios (delta C-13). Canopy dieback increased from 27% by volume in the spring of 2012 to 41% and 54% in 2013 and 2014, respectively. Tree mortality increased from 0% in 2012 to 6% and 10% in 2013 and 2014, respectively. Surprisingly, percent canopy dieback was not related to the number of defoliation events that ranged from 2 to 7 across the 10 sites prior to the 2013 growing season. On the other hand, canopy dieback increased with soil salinity in both 2013 (R-2 = 0.39, F = 5.07, P = 0.055) and 2014 (R-2 = 0.56, F = 10.26, P = 0.015). Canopy dieback in 2013 increased with bulk leaf delta C-13 (R-2 = 0.38, F = 4.08, P = 0.078), although delta C-13 also decreased with the number of defoliation events (R-2 = 0.64, F = 14.17, P = 0.0055), suggesting that photosynthetic rate or drought stress (as indicated by leaf delta C-13) may serve as a poor predictor for Tamarix canopy dieback in response to defoliation. Percent canopy dieback was correlated with shifts in NDVI measured from annual MODIS imagery (R-2 = 0.61, F = 12.32, P = 0.008), demonstrating that the tree surveys reflect site-scale changes in canopy cover. Results show that patterns of Tamarix canopy dieback and subsequent mortality following episodic defoliation by Diorhabda carinulata are likely to vary across broad gradients in soil salinity and other abiotic and biotic factors. Documented impacts of this biocontrol agent reported here will aid management efforts aimed at preserving riparian habitat in the short-term with conservation efforts targeting the removal and control of Tamarix over the long term.
机译:植物物种或种群应对食草动物的能力在很大程度上取决于资源可用性,生活史和适应性策略之间的复杂相互作用,以最大限度地防御食草动物。考虑到这些复杂的相互作用,经常很难预测到食草重复对植物胁迫和随后死亡的影响。为了更好地了解草食动物与环境条件之间的关系,我们研究了非本地灌木/树柳(Tamarix spp。)与专门的草食性动物(北柳叶甲虫(Diorhabda carinulata))之间的关系,后者作为Ta柳的生物防治剂而被释放。在美国西南部的维尔京河流域。甲虫仅以Tamarix叶子为食,导致完整的立木叶子脱水(即脱叶),持续数周。在三个连续的生长季节中,对10个地点的大约900种塔马柳植物进行了调查,以调查其冠层枯萎和死亡的情况,这些地点的落叶事件,树木高度,土壤盐分,土壤质地和叶片碳同位素比(δC-13)有所不同。冠层枯萎率从2012年春季的27%增至2013年和2014年的41%和54%。树木死亡率分别从2012年的0%增加到2013年和2014年的6%和10%。令人惊讶的是,在2013年生长季节之前的10个地点中,树冠死亡的百分率与2到7个落叶事件无关。另一方面,在2013年(R-2 = 0.39,F = 5.07,P = 0.055)和2014年(R-2 = 0.56,F = 10.26,P = 0.015),冠层的枯萎随着土壤盐分的增加而增加。 2013年,随着散叶三角洲C-13(R-2 = 0.38,F = 4.08,P = 0.078),冠层枯萎率有所增加,尽管三角洲C-13也随着落叶事件的发生而减少(R-2 = 0.64,F = 14.17,P = 0.0055),表明光合速率或干旱胁迫(如叶片δC-13所示)可能是落叶落叶响应Tamarix冠层回缩的较差预测指标。冠层枯萎的百分比与从年度MODIS影像测得的NDVI的变化相关(R-2 = 0.61,F = 12.32,P = 0.008),表明树木调查反映了冠层覆盖范围的站点尺度变化。结果表明,在土壤盐度和其他非生物和生物因素的宽梯度范围内,Di柳(Diorhabda carinulata)发生周期性的落叶后,mari柳冠层的死亡模式和随后的死亡率可能会有所不同。此处报道的这种生物防治剂的书面影响将有助于旨在短期内保护河岸栖息地的管理工作,而针对长期去除和控制Ta柳的保护工作将得到帮助。

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