入侵生境土壤对空心莲子草与马唐种间关系的反馈调节

Feedback regulation of soil within invaded habitats on the interspecific relationship between Alternanthera philoxeroides and Digitaria sanguinalis

  • 摘要: 【目的】 探讨空心莲子草入侵生境的土壤遗留效应对其自身及本土共生种马唐的反馈调节,为预测环境变化下空心莲子草入侵态势及实施生物替代提供参考依据。【方法】 通过在江西、湖南、广西和广东等4个省(区)空心莲子草入侵严重的生境采集土壤样品,并设置土壤处理对照处理、反馈处理(添加入侵生境土壤)、播种方式(单种、混种)和物种属性(马唐、空心莲子草)等3因子盆栽试验,探讨入侵生境土壤对空心莲子草及马唐在形态特征、生物量、营养和光合荧光等方面的影响。【结果】马唐的最大茎长、总碳和总氮含量显著(P<0.05,下同)或极显著(P<0.01,下同)高于空心莲子草,而空心莲子草的根面积、总生物量、地上生物量、地下生物量、根冠比、最小荧光(F0)、最大荧光(Fm)和光化学淬灭系数(qP-Lss)均显著或极显著高于马唐。与对照处理相比,反馈处理导致植物整体的最大茎长、根长、根面积和叶面积均极显著降低,且混种中空心莲子草根长的下降幅度高于马唐;反馈处理导致植物整体的总生物量、地上生物量和地下生物量均显著或极显著降低,马唐的根冠比极显著降低48.28%、空心莲子草的根冠比极显著提高20.10%;反馈处理导致马唐、空心莲子草的总碳含量分别极显著提高13.79%和148.00%;反馈处理导致植物整体的最大光量子效率(Fv/Fm)和马唐的光稳态实际光量子效率(QY-Lss)显著提高,且混种中空心莲子草的F0Fm分别显著降低45.40%和32.18%。【结论】大尺度空间上的空心莲子草入侵生境土壤削弱了其自身及马唐的形态和生物量,且种间竞争加剧了入侵生境土壤对空心莲子草光合荧光的负向反馈。当群落中存在本土植物马唐时,入侵生境土壤可能不利于空心莲子草的继发性入侵,可考虑在入侵区人工栽植马唐以实现对空心莲子草的替代控制。

     

    Abstract: 【Objective】 This study aimed to investigate the feedback regulation of soil legacy effects within Alternanthera philoxeroides-invaded habitats on itself and the native coexisting species Digitaria sanguinalis, so as to provide theoretical basis for predicting the invasion trends of Alternanthera philoxeroides under environmental changes and implementing biological substitution. 【Method】 Soil samples were collected from habitats seriously invaded by Alternanthera philoxeroides in four provinces (regions) of China, including Jiangxi, Hunan, Guangxi, and Guangdong. The three-factors potted experiment was conducted, which including the soil treatment (control treatment, feedback treatment (adding soil within invaded habitats), planting method (mono and mixed culture), and species trait (Digitaria sanguinalisAlternanthera philoxeroides), to examine the effects of soil within invaded habitats on the morphological trait, biomass, nutrition, and photosynthetic fluorescence of Alternanthera philoxeroides and Digitaria sanguinalis. 【Result】 The maximum stem length, content of total carbon and total nitrogen in Digitaria sanguinalis were significantly (P<0.05, the same below) or extremely significantly (P<0.01, the same below) higher than those in Alternanthera philoxeroides, while the root area, total biomass, shoot biomass, root biomass, root-shoot ratio, minimum fluorescence (F0), maximum fluorescence (Fm), and photochemical quenching coefficient (qP-Lss) of Alternanthera philoxeroides were significantly or extremely significantly higher than those of Digitaria sanguinalis. Compared with the control treatment, feedback treatment led to extremely significant decrease in the maximum stem length, root length, root area, and leaf area of the entire stu-died plants, and caused a higher decrease in the root length of Alternanthera philoxeroides than that of Digitaria sanguinalis in mixed cultures. Feedback treatment led to significant or extremely significant decrease in the total biomass, shoot biomass, and root biomass of the entire studied plants, caused an extremely significant decrease of 48.28% in the root-shoot ratio of Digitaria sanguinalis and an extremely significant increase of 20.10% in that of Alternanthera philoxeroides. Feedback treatment led to an extremely significant increase of 13.79% and 148.00% in the total carbon of Digitaria sanguinalis and Alternanthera philoxeroides respectively. Feedback treatment led to significant increase in the maximum light quantum efficiency (Fv/Fm) of the entire studied plants and the steady-state light actual quantum efficiency (QY-Lss) of Digitaria sanguinalis, while caused significant decrease of 45.40% and 32.18% in F0 and Fm of Alternanthera philoxeroides in mixed cultures respectively. 【Conclusion】 Soil within Alternanthera philoxeroides-invaded habitats on large scale weakens the morphology and biomass of itself and Digitaria sanguinalis, and interspecific competition intensifies the negative feedback of soil within invaded-habitats on photosynthetic fluorescence of Alternanthera philoxeroides. Thus, when the native species Digitaria sanguinalis exists in communities, soil within invaded habitats may not be conducive to the secondary invasion of Alternanthera philoxeroides, and the artificial planting of Digitaria sanguinalis in invasion areas can be considered as a method for substitutive control of A. philoxeroides.

     

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