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模拟氮沉降和施加生物炭对香榧成花强度的影响

The Effects of Simulated Nitrogen Deposition and Biochar Application on Flowering Intensity of Torreya grandis

  • 摘要:
    目的 探究模拟氮沉降和施加生物炭对香榧成花强度的影响及其生理调控机制,为氮沉降背景下香榧产业的生态适应性管理提供理论支撑。
    方法 以香榧结果植株为研究对象,采用2 × 3双因子交叉试验设计,设置3个氮沉降梯度(0、30和60 kg·N·hm−2·a−1)和2个生物炭梯度(0和40 t·hm−2)。测定不同处理下香榧成花强度、叶片碳氮代谢指标养分和土壤理化性质,分析氮沉降和生物炭对香榧成花强度影响机制及其交互关系。
    结果 ①氮沉降呈现剂量效应,与对照组(CK)相比,低氮使成花强度提高3.51%,而高氮导致成花强度降低9.27%;生物炭单独施用显著提高成花强度(29.58%,p<0.05)且能缓解高氮对成花强度的不利影响,高氮 + 生物炭处理较单施高氮显著提高19.34%(p<0.05)。②模拟氮沉降和生物炭处理显著影响土壤养分状况,其中在高氮条件下施加生物炭,能显著提高成花启动期(11月)和花器官发育期(次年3月)土壤pH值、碱解氮、有机质和速效钾含量(p<0.05)。③叶片养分分析表明,与单一的氮沉降处理相比,11月氮沉降和生物炭复合处理显著提高叶片可溶性蛋白含量(低氮 + 生物炭:50.69%,高氮 + 生物炭:78.59%,p<0.05),显著降低淀粉含量(低氮 + 生物炭:62.64%,高氮 + 生物炭:34.91%,p<0.05);次年3月,高氮 + 生物炭显著提高叶片可溶性蛋白含量(19.59%,p<0.05),而低氮 + 生物炭则显著提高叶片淀粉含量(19.79%,p<0.05)。④成花强度与叶片可溶性蛋白(11月)、可溶性糖(次年3月)含量及土壤pH(11月、次年3月)均显著相关(p<0.05),表明碳氮代谢和土壤酸碱调节可能是影响成花强度的重要因素。
    结论 氮沉降对香榧成花强度的影响具有浓度依赖性,适度氮沉降促进成花,过量则抑制成花。生物炭通过改善土壤pH和调节植株碳氮养分,有效缓解氮沉降的负面影响并提高成花强度。建议在氮沉降高发区于成花关键期(11月至翌年3月)实施生物炭与养分联合管理,以应对氮沉降的不利影响。

     

    Abstract:
    Objective This study aimed to investigate the effects of simulated nitrogen deposition and biochar application on flowering intensity of Torreya grandis and its physiological regulatory mechanisms, providing theoretical support for ecological adaptive management of T. grandis under nitrogen deposition scenarios.
    Methods A 2 × 3 factorial experimental design was conducted on fruit-bearing T. grandis trees, with three nitrogen deposition gradients (0, 30, and 60 kg·N·ha−1·a−1) and two biochar gradients (0 and 40 t·ha−1). Flowering intensity, leaf carbon-nitrogen metabolic indicators, and soil physicochemical properties were measured under each treatment to analyze the mechanisms and interactive effects of nitrogen deposition and biochar on flowering intensity.
    Results ① Nitrogen deposition exhibited dose-dependent effects: compared with the control (CK), low nitrogen increased flowering intensity by 3.51%, while high nitrogen decreased it by 9.27%. Biochar application alone significantly increased flowering intensity by29.58% (p<0.05) and alleviated the adverse effects of high nitrogen. The combined high nitrogen + biochar treatment significantly increased flowering intensity by 19.34% compared to high nitrogen alone (p<0.05). ② Nitrogen deposition and biochar treatments significantly affected soil nutrient status. Biochar application under high nitrogen deposition significantly improved soil pH, alkali-hydrolyzed nitrogen, organic matter, and available potassium contents during both the flowering initiation period (November) and flower organ development period (March of the following year) (p<0.05). ③ Leaf nutrient analysis revealed that combined nitrogen deposition and biochar treatment significantly increased soluble protein content (by 50.69% under high nitrogen + biochar, and 78.59% under low nitrogen + biochar: p<0.05) and reduced starch content (by 62.64% and 34.91%, respectively, p<0.05) in November. In March, high nitrogen + biochar significantly increased soluble protein content by 19.59% (p<0.05), while low nitrogen + biochar significantly increased starch content by 19.79% (p<0.05). ④ Flowering intensity was significantly correlated with leaf soluble protein, soluble sugar contents, and soil pH and nutrient indicators (p<0.05), suggesting that carbon-nitrogen metabolism and soil pH regulation are key factors influencing flowering intensity.
    Conclusion The effects of nitrogen deposition on flowering intensity of T. grandis are concentration-dependent, with moderate nitrogen deposition promoting flowering and excessive nitrogen deposition inhibiting it. Biochar effectively alleviates the negative impacts of nitrogen deposition and enhances flowering intensity by improving soil pH and regulating plant carbon-nitrogen nutrients. It is recommended to implement combined biochar and nutrient management during the critical flowering period (November to March of the following year) in areas with high nitrogen deposition to mitigate its adverse effects.

     

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