Institute of Ecology, College of Urban and Environmental Sciences, Key Laboratory for Earth Surface Processes of the Ministry of Education, Peking University, Beijing 100871, China.
School of Geographical Sciences, Fujian Normal University, Fuzhou 350117, China.
Sci Total Environ. 2024 Jan 15;908:168350. doi: 10.1016/j.scitotenv.2023.168350. Epub 2023 Nov 5.
Priming effect (PE) plays a crucial role in regulating the decomposition of soil organic matter (SOM). Multiple empirical results have shown that nitrogen (N) and phosphorus (P) addition can significantly alter the direction and intensity of PE, which may significantly affect carbon turnover in grasslands, especially in alpine meadows that are sensitive to N and P enrichment. To evaluate the PE responses to N and/or P addition, we conducted an incubation experiment by adding C-labeled glucose and nutrient additions (+N, +P, and +NP) in soils collected from an alpine meadow. The soils were incubated for 30 days and soil/microbial properties and enzyme activities were measured. Partial correlation and linear regression analyses were then performed to investigate their correlations with PE. The results showed that mean PE intensity among all treatments was 0.61 mg C g soil or 1.35 (ratio). Nitrogen addition increased PE intensity, which was attributed to the better match between soil resources and microbial demands and enhanced enzyme activities. However, the PE intensity in P-addition soils was lower than that in control soils. This discrepancy may be related to the P-induced decrease of N availability and stronger microbial C/N imbalance. No significant response of PE intensity to NP addition was detected, and this could be explained by the offset of positive N effects and negative P effects on microbial decomposition. In this experiment, N or P addition altered the PE intensity by mediating the match between soil C:N:P ratio and microbial demands, which supported the stoichiometric decomposition hypothesis. Overall, our study highlights the importance of considering the C, N and P coupling in regulating PE, and underscores the need for further investigation into the effects of soil P on microbial activity and SOM decomposition.
启动效应(PE)在调节土壤有机质(SOM)分解中起着至关重要的作用。多项实证研究表明,氮(N)和磷(P)的添加可以显著改变 PE 的方向和强度,这可能会显著影响草地的碳周转,特别是对 N 和 P 富集敏感的高山草甸。为了评估 N 和/或 P 添加对 PE 的响应,我们在高山草甸采集的土壤中进行了添加 C 标记葡萄糖和养分添加(+N、+P 和+NP)的培养实验。土壤在 30 天内进行培养,并测量土壤/微生物特性和酶活性。然后进行偏相关和线性回归分析,以研究它们与 PE 的相关性。结果表明,所有处理的平均 PE 强度为 0.61mg C g 土壤或 1.35(比值)。氮添加增加了 PE 强度,这归因于土壤资源与微生物需求的更好匹配以及酶活性的增强。然而,P 添加土壤中的 PE 强度低于对照土壤。这种差异可能与 P 诱导的 N 可用性降低和更强的微生物 C/N 失衡有关。NP 添加对 PE 强度没有显著响应,这可以解释为微生物分解过程中 N 效应的正效应和 P 效应的负效应的抵消。在本实验中,N 或 P 的添加通过调节土壤 C:N:P 比与微生物需求的匹配来改变 PE 强度,这支持了化学计量分解假说。总体而言,我们的研究强调了在调节 PE 时考虑 C、N 和 P 耦合的重要性,并强调需要进一步研究土壤 P 对微生物活性和 SOM 分解的影响。