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亚热带两种森林土壤净氮矿化速率对温度升高的响应

周子寒, 方晰, 朱小叶   

  1. 中南林业科技大学生态环境学院, 长沙 410004生态环境学院, 41004
    湖南会同杉木林生态系统国家野外科学观测研究站, 湖南会同 438107生态环境学院, 438107
    湖南省第三测绘院, 长沙 410011第三测绘院, 410011
    湖南省地理空间信息工程技术研究中心, 长沙 410011地理空间信息工程技术研究中心, 410011
  • 收稿日期:2025-07-01 修回日期:2025-09-02

Response of soil net nitrogen mineralization rate to temperature variations in two subtropical forest ecosystems

ZHOU ZiHan ZiHan, FANG Xi Xi, ZHU XiaoYe XiaoYe   

  1. College of Ecology and Environment, Central South University of Forestry and Technology, Changsha 410004, China 41004,
    College of Ecology and Environment, Huitong National Field Station for Scientific Observation and Research of Chinese Fir Plantation Ecosystem in Hunan Province, Huitong 438107, China 438107,
    The Third Surveying and Mapping Institute, The Third Surveying and Mapping Institute of Hunan Province, Changsha 410011, China 410011,
    Geospatial Information Engineering and Technology Research Center, Hunan Geospatial Information Engineering and Technology Research Center, Changsha 410011,China 410011,
  • Received:2025-07-01 Revised:2025-09-02
  • Supported by:
    Supported by the National Natural Science Foundation of China(U23A20154)

摘要: 全球变暖深刻影响森林土壤氮(N)循环,但其对不同森林类型土壤N矿化过程(氨化、硝化)的影响方向(促进或抑制)及温度敏感性(Q10)尚不明确。本研究选取湘中东丘陵区马尾松针阔混交林(PLL)和石栎-青冈常绿阔叶林(LCC),采用室内恒温培养法(10、25、30、40 ℃),测定0—10 cm和10—20 cm土层净氨化速率(NAR)、净硝化速率(NNR)和净N矿化速率(NMR),通过指数模型拟合矿化速率与温度的关系计算Q10,并分析其与生物因子和非生物因子的关系。结果表明:(1) 温度与森林类型、土层深度交互作用显著,表现在:LCC的NAR、NNR和NMR普遍显著高于PLL,且差异随土层和温度(尤其对NNR)变化;两种森林土壤NAR、NMR均随温度升高而显著增加,NNR则在30 ℃达峰值后下降;所有速率均随土层加深而降低,且表层(0—10 cm)土壤矿化速率在高温下的优势更显著;土壤氨氧化微生物活性在30~40 ℃最强,而硝化微生物活性在10~25 ℃最强,导致NNR在高温(40 ℃)下下降。(2) PLL各土层NAR-Q10(2.00—2.01)、NMR-Q10(2.01—2.02)均显著高于LCC(1.89—1.95和1.93—1.94),表明PLL土壤N转化对升温更敏感。仅在LCC的10—20 cm土层中,NAR-Q10显著高于其表层(0—10 cm)土壤。(3) NAR主要受凋落物层碳氮比和土壤全氮调控;NNR和NMR主要由微生物生物量磷(MBP)和凋落物层全氮驱动;NAR-Q10主要受MBP和脲酶活性影响;而NMR-Q10则主要受土壤无机氮调控。综上,升温显著促进亚热带森林土壤N矿化过程(NNR在>30 ℃除外),且PLL土壤N矿化的Q10高于LCC。LCC表现出更高的N矿化速率和更低的温度敏感性,凸显了保护现有天然林对维持土壤N循环稳定及应对气候变化的重要性。本研究为理解亚热带森林土壤N循环对气候变化的响应机制及优化森林管理措施提供了科学依据。

关键词: 马尾松针阔混交林, 石栎-青冈常绿阔叶林, 温度敏感性, 氨化速率, 硝化速率

Abstract: Global warming profoundly affects the nitrogen (N) cycle in forest soils, but the direction of its impact (promotion or inhibition) on soil N mineralization processes (ammonification and nitrification) in different forest types and its temperature sensitivity (Q10) remain unclear. This study selected Pinus massoniana mixed conifer-broadleaf forest (PLL) and Lithocarpus glaber-Cyclobalanopsis glauca evergreen broad-leaved forest (LCC) in the hilly areas of central-southern Hunan Province. Using a constant-temperature incubation method at 10, 25, 30, and 40 ℃, the net ammonification rate (NAR), net nitrification rate (NNR), and net N mineralization rate (NMR) in the 0—10 cm and 10—20 cm soil layers were measured. The relationship between the mineralization rate and temperature was fitted by an exponential model to calculate Q10, and the relationships with biological and abiotic factors were analyzed. The results showed that: (1) The interaction between temperature and forest type and soil depth was significant, manifested as: the NAR, NNR, and NMR of LCC were generally significantly higher than those of PLL, and the differences varied with soil depth and temperature (especially for NNR); the NAR and NMR of both forest soils increased significantly with increasing temperature, while NNR reached a peak at 30 ℃ and then decreased; all rates decreased with increasing soil depth, and the advantage of soil mineralization rate in the surface layer (0-10 cm) was more significant at high temperatures; the activity of soil ammonia-oxidizing microorganisms was the strongest at 30~40 ℃, while the activity of nitrifying microorganisms was the strongest at 10~25 ℃, resulting in a decrease in NNR at high temperatures (40 ℃). (2) The NAR-Q10 (2.00—2.01) and NMR-Q10 (2.01—2.02) of all soil layers in PLL were significantly higher than those in LCC (1.89—1.95 and 1.93—1.94), indicating that the N transformation in PLL soil was more sensitive to warming. Only in the 10—20 cm soil layer of LCC was the NAR-Q10 significantly higher than that in the surface layer (0—10 cm) soil. (3) NAR was mainly regulated by the carbon-nitrogen ratio of the litter layer and soil total nitrogen; NNR and NMR were mainly driven by microbial biomass phosphorus (MBP) and total nitrogen in the litter layer; NAR-Q10 was mainly affected by MBP and urease activity; while NMR-Q10 was mainly regulated by soil inorganic nitrogen. In conclusion, warming significantly promoted the N mineralization process in subtropical forest soils (except for NNR at >30 ℃), and the Q10 of N mineralization in PLL soil was higher than that in LCC. LCC showed higher N mineralization rates and lower temperature sensitivity, highlighting the importance of protecting existing natural forests for maintaining the stability of the soil N cycle and responding to climate change. This study provides a scientific basis for understanding the response mechanism of the soil N cycle in subtropical forests to climate change and optimizing forest management measures.

Key words: Pinus massoniana mixed conifer-broadleaf forest, Lithocarpus glaber-Cyclobalanopsis glauca evergreen broad-leaved forest, temperature sensitivity, net ammonification rate, net nitrification rate