碳基造粒、土壤撕裂和除草剂应用可用于克服灰臭木(Jacksonia furcellata)的植物招募障碍。

V. Brown, T. E. Erickson, R. Hobbs, Stanley Mastrantonis, A. Ritchie
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引用次数: 0

摘要

由于来自入侵植物物种的竞争和恶劣的土壤条件,基于种子的恢复努力往往收效甚微。我们的目标是通过结合碳基种子增强技术和常用的恢复管理实践来缓解这些植物招募障碍。与非颗粒(对照)种子相比,我们在西澳大利亚Banksia林地常见的多年生灌木灰臭木(Jacksonia furcellata)上测试了七种种子增强技术,包括挤压颗粒、涂层和硬币(一种新型挤压方法),并与活性炭或生物炭结合。我们在两个地点(后沙坑和后松林)测试了五种管理方法,包括除草剂和土壤撕裂的组合。在松树后地点,含有生物炭的硬币总体平均出苗率最高(53%),而在矿后地点,含有活性炭的挤压颗粒的平均出苗率最高(58%)。相比之下,未成粒种子的出苗率明显较低(分别为44%和45%)。在矿后现场,生物炭硬币的存活率(31%)也高于未制成颗粒的种子(22%),与未施用管理措施的对照(16%)相比,在施用除草剂后拔土的地块(36%)的存活率最高。在松林后,幼苗成活率较差(<10%),种子处理和管理措施对幼苗成活率没有显著影响。采用基于碳的种子处理和管理方法,例如在施用除草剂后进行土壤撕裂,可能有助于克服直接播种计划中的出苗瓶颈。然而,在种子增强技术用于大规模播种计划之前,需要对幼苗存活进行进一步研究,特别是在高度退化的环境中。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
Carbon‐based pelleting, soil ripping and herbicide application can be used to overcome plant recruitment barriers in Grey Stinkwood (Jacksonia furcellata)
Seed‐based restoration efforts frequently experience limited success due to competition from invasive plant species and poor soil conditions. We aimed to alleviate these plant recruitment barriers through a combination of carbon‐based seed enhancement technologies and commonly applied restoration management practices. Compared to non‐pelleted (control) seeds, we tested seven seed enhancement technologies on Grey Stinkwood (Jacksonia furcellata), a perennial shrub common within the Banksia Woodlands of Western Australia, which included extruded pellets, coating and coins (a novel extrusion method), incorporated with activated carbon or biochar. We tested five management practices including combinations of herbicide and soil ripping at two locations (post‐sand mine and Post‐pine plantation). At the Post‐pine site, coins incorporating biochar had the highest overall mean emergence (53%), and at the Post‐mine site, extruded pellets containing activated carbon had the highest mean emergence (58%). In comparison, emergence was significantly lower from the non‐pelleted seeds (44% and 45% respectively). Survival at the Post‐mine site was also higher from biochar coins (31%) compared to the non‐pelleted seeds (22%), and highest in plots with herbicide application followed by soil ripping (36%), compared to the control, in which no management practice was applied (16%). At the Post‐pine site, survival was poor (<10%), and seed treatment and management practice did not significantly affect seedling survival. Using carbon‐based seed treatments and management practices, such as herbicide application followed by soil ripping, may help to overcome seedling emergence bottlenecks in direct seeding programmes. However, further examination into seedling survival is required, particularly within highly degraded settings, before seed enhancement technologies are used in large‐scale seeding programmes.
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