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Edaphic constraints on seed germination and emergence of three Acacia species for dryland restoration in Saudi Arabia

机译:沙特阿拉伯中旱地旱地三种合欢种萌发和三种合欢种萌发的仿生约束

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In situ edaphic factors affecting seed germination and seedling emergence of three framework species of Acacia were investigated with the intent of developing fundamental and scalable restoration capacity for Arabian dryland restoration. Direct seeding represents the most efficient means to restore vegetation at the landscape scale and this study provides insight into edaphic and ecological limitations, as well as effective protocols governing the use of native seeds for restoration in hyper-arid environments. The study was conducted in extant Acacia woodland habitat on conserved land (Thumamah Nature Park) in close proximity to Riyadh, Saudi Arabia. Broad-scale direct seeding using un- and pretreated Acacia gerrardii, A. tortilis, and A. ehrenbergiana seed, and two seed burial depths were implemented across three sites with distinct soil surface characteristics. Eight weeks post-sowing, random samples for each species x seed treatment x burial depth combination were excavated, sieved, and categorized as follows: failed to germinate, germinated but died prior to emerging, or successfully emerged. We show that germination and emergence of Acacia gerrardii, A. tortilis, and A. ehrenbergiana were driven by a three-way interaction among species, site, and seed burial depth. Treating seed with the signaling compound Moddus did not have a definitive effect, positive or negative, on any of the species investigated. Acacia gerrardii was the only species that exhibited widespread emergence, though emergence was not consistent across sites or burial depths. Germination was highest in disturbed soil (up to 69% for A. gerrardii), but very few ( 2%) successfully emerged; a greater proportion of germinants in sandy soil emerged (up to 44% for A. gerrardii) even though the overall germination was less. Though species-dependent, a 2-cm sowing depth was most effective in sand; while in disturbed soil, sowing depths of 1 and 2 cm were comparable; and no germination was observed in gravelly clay soil. Sandy soil exhibited rapid water infiltration (107.6 mm min(-1)), and post-sowing surface crusting was a non-factor (0.44 kg cm(-2)). Disturbed soil exhibited moderate water infiltration (1.46 mm min(-1)) and post-sowing surface crusting was double that of sand (0.88 kg cm(-2)) and restrictive on seedling emergence. Gravelly clay exhibited extremely poor water infiltration (0.12 mm min(-1)), and surface crusting was severe (4.49 kg cm(-2)) and an order of magnitude greater than sand. The medium-coarse sand fraction, a key driver of the observed soil surface processes, was greatest in sand (55%) and significantly less and uniform in the disturbed (22%) and gravelly clay (22%) soils. Our findings demonstrate that soil surface characteristics and associated processes can dictate ecological processes at depths as shallow as 1-2 cm, and that soil crusts that slow water infiltration and impede seedling emergence rapidly reconstitute after disturbance; both are important considerations for restoring dryland vegetation.
机译:在原地的辅助因素中,研究了三种骨架种类的种子萌发和幼苗出现的合理物种的意图,提出了阿拉伯旱地恢复的基本和可扩展的恢复能力。直接播种代表恢复景观量表中植被的最有效手段,本研究提供了对辅助和生态局限性的洞察力,以及有效的协议,用于在超干旱环境中恢复原植种子。该研究在现存的Acacia林地栖息地进行了保守的土地(Thumamah自然公园),靠近沙特阿拉伯利雅得。使用未处理和预处理的Acacia Gerrardii,A. Tortilis和A. ehrenbergiana种子和两个种子埋藏深度的宽阔直接播种在三个地点实施了不同的土壤表面特征。播种后八周,每种物种的随机样品x种子处理x埋藏深度组合被挖掘,筛分,并分类如下:未发生发芽,发芽但在出现之前萌发,或者成功出现。我们展示了Acacia Gerrardii,A. Tortilis和A. Ehrenbergiana的萌芽和出现是由物种,网站和种子埋葬深度之间的三种互动驱动的。用信号化合物Moddus治疗种子没有明确的效果,阳性或阴性在任何研究中所研究的任何物种。 Acacia Gerrardii是唯一一个展示普遍出现的物种,但横跨网站或埋葬深度的出现并不一致。萌发在扰动的土壤中最高(A.Gerrardii高达69%),但成功地出现了很少(&lt 2%);即使整体发芽较少,砂土中的发芽剂更大比例的发芽剂(达44%)。虽然物种依赖,但2厘米的播种深度在沙子中最有效;虽然在干扰的土壤中,播种深度为1和2厘米的比较;在砾石粘土土壤中没有观察到发芽。沙质土壤表现出快速的水渗透(107.6mm min(-1)),播种表面壳是非因子(0.44kg cm(-2))。令人不安的土壤表现出中度水渗透(1.46mm min(-1)),播种表面壳是砂(0.88kg cm(-2))的两倍,并限制幼苗出苗。砾石粘土表现出极差的水渗透(0.12mm min(-1)),表面壳严重(4.49kg cm(-2)),大于沙子的数量级。中等粗砂馏分是观察到的土壤表面过程的关键驱动器,在砂(55%)中最大,在干扰(22%)和砾石粘土(22%)土壤中显着较低和均匀。我们的研究结果表明,土壤表面特征和相关过程可以在深度为1-2厘米的深度下决定生态过程,并且土壤渗透缓慢渗透并阻碍苗木出现迅速重建;两者都是恢复旱地植被的重要考虑因素。

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