Key Laboratory of Vegetation Restoration and Management of Degraded Ecosystems, Guangdong Provincial Key Laboratory of Applied Botany, South China Botanical Garden, Chinese Academy of Sciences, Guangzhou, China; South China National Botanical Garden, Guangzhou, China.
Key Laboratory of Vegetation Restoration and Management of Degraded Ecosystems, Guangdong Provincial Key Laboratory of Applied Botany, South China Botanical Garden, Chinese Academy of Sciences, Guangzhou, China; South China National Botanical Garden, Guangzhou, China; College of Resource and Environment, University of Chinese Academy of Sciences, Beijing, China.
Sci Total Environ. 2023 Jun 15;877:162965. doi: 10.1016/j.scitotenv.2023.162965. Epub 2023 Mar 21.
The traditional view holds that biological nitrogen (N) fixation is energetically expensive and thus, facultative N fixers reduce N fixation rates while obligate N fixers are excluded by non-N fixers as soil N becomes rich. This view, however, contradicts the phenomenon that N fixation does not decline in many terrestrial ecosystems under N enrichment. To address this paradoxical phenomenon, we conducted a meta-analysis of N fixation and diazotroph (N-fixing microorganism) community structure in response to N addition across terrestrial ecosystems. N addition inhibited N fixation, but the inhibitory effect weakened across increased soil organic carbon (SOC) concentrations. The response ratios of N fixation (including free-living, plant-associated, and symbiotic types) to N addition were lower in the ecosystems with low SOC concentrations (<10 mg/g) than in those with medium or high SOC concentrations (10-20 and > 20 mg/g, respectively). The negative N-addition effects on diazotroph abundance and diversity also weakened across increased SOC levels. Among the climatic and soil factors, SOC was the most important predictor regarding the responses of N fixation and diazotroph community structure to N addition. Overall, our study reveals the role of SOC in affecting the responses of N fixation to N addition, which helps understand the relationships of biological N fixation and N enrichment as well as the mechanisms of terrestrial C and N coupling.
传统观点认为生物固氮(N)是能量密集型的,因此,兼性固氮生物会降低固氮速率,而当土壤 N 变得丰富时,专性固氮生物则会被非固氮生物所排斥。然而,这种观点与氮富集下许多陆地生态系统中固氮不会下降的现象相矛盾。为了解决这一矛盾现象,我们对陆地生态系统中氮添加对固氮和固氮生物(固氮微生物)群落结构的影响进行了荟萃分析。氮添加抑制了固氮作用,但随着土壤有机碳(SOC)浓度的增加,抑制作用减弱。在 SOC 浓度较低(<10 mg/g)的生态系统中,固氮(包括自由生活、植物相关和共生类型)对氮添加的响应比 SOC 浓度中等或较高(10-20 和>20 mg/g)的生态系统中的响应比更低。氮添加对固氮生物丰度和多样性的负效应也随着 SOC 水平的增加而减弱。在气候和土壤因素中,SOC 是影响固氮和固氮生物群落结构对氮添加响应的最重要预测因子。总体而言,我们的研究揭示了 SOC 在影响固氮对氮添加响应中的作用,这有助于理解生物固氮与氮富集的关系以及陆地碳氮耦合的机制。