Wu Jiangqi, Wang Haiyan, Li Guang, Chen Nan
Key Laboratory of Grassland Ecosystem (Gansu Agricultural University), Ministry of Education, Gansu Agricultural University, Lanzhou, 730070, China.
College of Forestry, Gansu Agricultural University, Lanzhou, 730070, China.
Sci Rep. 2024 Dec 30;14(1):31848. doi: 10.1038/s41598-024-83285-8.
Soil nitrogen (N) transformation is an essential portion of the N cycle in wetland ecosystems, governing the retention status of soil N by controlling the effective soil N content. N deposition produced by human activities changes the physical characteristics of soil, affecting N fractions and enzyme activities. To characterize these influences, three different N addition levels (N5, 5 g/m; N10, 10 g/m; N15, 15 g/m) were established using a wet meadow on the Qinghai-Tibet Plateau (QTP) as a control treatment (0 g/m). We investigated the features of soil physical property alterations, N fractions contents, and enzyme activities under N addition conditions throughout the peak plant growth season. Our findings indicated that N addition significantly enhanced soil aeration, porosity, total nitrogen (TN), ammonium nitrogen (NH), nitrate nitrogen (NO) content, and urease activity. At the same time, it decreased soil dissolved organic nitrogen (DON) content and bulk density (BD). Additionally, N addition treatment exerted a significant seasonal impact on soil nitrogen component content. The nitrogen component content within the surface soil (0-10 cm) under four treatments is more sensitive to N addition, whereas the nitrogen component in the deep soil is relatively stable. Principal component analysis demonstrated that soil aeration and porosity were the primary factors affecting soil N fractions and enzyme activities. The findings suggested that lower levels of N addition promoted the transformation process of soil N pools in wet meadows and exacerbated the loss of N in wetland ecosystems. Our findings indicate that sustained increases in N deposition will accelerate soil microbial N cycling, potentially overcoming N limitation in alpine wetland ecosystems and exacerbating the risk of N loss and greenhouse gas emissions from alpine wetland surface soils.
土壤氮(N)转化是湿地生态系统氮循环的重要组成部分,通过控制土壤有效氮含量来决定土壤氮的保留状态。人类活动产生的氮沉降改变了土壤的物理特性,影响氮组分和酶活性。为了表征这些影响,以青藏高原(QTP)的湿草甸作为对照处理(0 g/m),设置了三种不同的氮添加水平(N5,5 g/m;N10,10 g/m;N15,15 g/m)。我们在植物生长旺季研究了氮添加条件下土壤物理性质变化、氮组分含量和酶活性的特征。我们的研究结果表明,氮添加显著提高了土壤通气性、孔隙度、总氮(TN)、铵态氮(NH)、硝态氮(NO)含量和脲酶活性。同时,它降低了土壤溶解有机氮(DON)含量和容重(BD)。此外,氮添加处理对土壤氮组分含量有显著的季节影响。四种处理下表层土壤(0 - 10 cm)中的氮组分含量对氮添加更为敏感,而深层土壤中的氮组分相对稳定。主成分分析表明,土壤通气性和孔隙度是影响土壤氮组分和酶活性的主要因素。研究结果表明,较低水平的氮添加促进了湿草甸土壤氮库的转化过程,并加剧了湿地生态系统中的氮损失。我们的研究结果表明,氮沉降的持续增加将加速土壤微生物氮循环,可能克服高山湿地生态系统中的氮限制,并加剧高山湿地表层土壤氮损失和温室气体排放的风险。