{"title":"Differential Responses of Soil Phosphorus Fractions to Nitrogen and Phosphorus Fertilization: A Global Meta-Analysis","authors":"Qingshui Yu, Frank Hagedorn, Josep Penuelas, Jordi Sardans, Xiangping Tan, Zhengbing Yan, Chenqi He, Xiaofeng Ni, Yuhao Feng, Jiangling Zhu, Chengjun Ji, Zhiyao Tang, Mai-He Li, Jingyun Fang","doi":"10.1029/2023GB008064","DOIUrl":null,"url":null,"abstract":"<p>Anthropogenic inputs of nitrogen (N) and phosphorus (P) to terrestrial ecosystems alter soil nutrient cycling. However, the global-scale responses of soil P fractions to N and P inputs and their underlying mechanisms remain elusive. We conducted a global meta-analysis based on 818 observations of soil P fractions from 99 field N and P addition experiments in forest, grassland, and cropland ecosystems ranging from temperate to tropical zones. Our global meta-analysis revealed distinct responses of soil P fractions to N and P enrichment. For studies using the Chang and Jackson inorganic (Pi) method, we found that high N addition promoted the transformation of immobile Pi fractions into Ferrum/Aluminum-bound Pi and available Pi in surface soils through soil acidification. However, this acid-induced transformation of Pi fractions by N addition was observed only in Calcium-rich soils, while in acidic soils, further acidification led to increase P binding. In contrast, additions of P alone or combined with N significantly increased all soil Pi fractions. Regarding the Hedley P fractions, N addition generally decreased labile organic P by enhancing soil acid phosphatase activity. The responses of other P fractions were influenced by soil pH, fertilization rates, ecosystem type, and other factors. P addition increased most soil P fractions. Overall, both P fractionation methods consistently demonstrate that N inputs deplete soil P and accelerate P cycling, while P inputs increase most soil P fractions, alleviating P limitation. These findings are crucial for predicting the effects of future atmospheric N and P deposition on P cycling processes.</p>","PeriodicalId":12729,"journal":{"name":"Global Biogeochemical Cycles","volume":"38 7","pages":""},"PeriodicalIF":5.4000,"publicationDate":"2024-07-28","publicationTypes":"Journal Article","fieldsOfStudy":null,"isOpenAccess":false,"openAccessPdf":"","citationCount":"0","resultStr":null,"platform":"Semanticscholar","paperid":null,"PeriodicalName":"Global Biogeochemical Cycles","FirstCategoryId":"89","ListUrlMain":"https://onlinelibrary.wiley.com/doi/10.1029/2023GB008064","RegionNum":2,"RegionCategory":"地球科学","ArticlePicture":[],"TitleCN":null,"AbstractTextCN":null,"PMCID":null,"EPubDate":"","PubModel":"","JCR":"Q1","JCRName":"ENVIRONMENTAL SCIENCES","Score":null,"Total":0}
引用次数: 0
Abstract
Anthropogenic inputs of nitrogen (N) and phosphorus (P) to terrestrial ecosystems alter soil nutrient cycling. However, the global-scale responses of soil P fractions to N and P inputs and their underlying mechanisms remain elusive. We conducted a global meta-analysis based on 818 observations of soil P fractions from 99 field N and P addition experiments in forest, grassland, and cropland ecosystems ranging from temperate to tropical zones. Our global meta-analysis revealed distinct responses of soil P fractions to N and P enrichment. For studies using the Chang and Jackson inorganic (Pi) method, we found that high N addition promoted the transformation of immobile Pi fractions into Ferrum/Aluminum-bound Pi and available Pi in surface soils through soil acidification. However, this acid-induced transformation of Pi fractions by N addition was observed only in Calcium-rich soils, while in acidic soils, further acidification led to increase P binding. In contrast, additions of P alone or combined with N significantly increased all soil Pi fractions. Regarding the Hedley P fractions, N addition generally decreased labile organic P by enhancing soil acid phosphatase activity. The responses of other P fractions were influenced by soil pH, fertilization rates, ecosystem type, and other factors. P addition increased most soil P fractions. Overall, both P fractionation methods consistently demonstrate that N inputs deplete soil P and accelerate P cycling, while P inputs increase most soil P fractions, alleviating P limitation. These findings are crucial for predicting the effects of future atmospheric N and P deposition on P cycling processes.
人类活动向陆地生态系统输入的氮(N)和磷(P)改变了土壤养分循环。然而,全球范围内土壤磷组分对氮和磷输入的反应及其内在机制仍然难以捉摸。我们根据从温带到热带地区的森林、草地和耕地生态系统中 99 次田间氮和磷添加实验的 818 次土壤磷组分观测结果进行了全球荟萃分析。我们的全球荟萃分析揭示了土壤磷组分对氮和磷富集的不同反应。在使用 Chang 和 Jackson 无机(Pi)方法进行的研究中,我们发现高氮添加会通过土壤酸化促进表层土壤中不可移动的 Pi 部分转化为铁/铝结合的 Pi 和可用的 Pi。然而,只有在富钙土壤中才能观察到这种由添加氮引起的钙馏分酸性转化,而在酸性土壤中,进一步酸化会导致钙结合增加。与此相反,单独添加钾或结合添加氮都会显著增加土壤中的钾馏分。关于 Hedley P 组分,添加氮通常会通过提高土壤酸性磷酸酶活性来减少可溶性有机钾。其他钾组分的反应受土壤 pH 值、施肥量、生态系统类型和其他因素的影响。磷的添加增加了大多数土壤中的磷组分。总之,这两种磷分馏方法一致表明,氮的输入会消耗土壤中的磷并加速磷的循环,而磷的输入会增加土壤中大部分的磷分馏,从而缓解磷的限制。这些发现对于预测未来大气中氮和磷沉积对磷循环过程的影响至关重要。
期刊介绍:
Global Biogeochemical Cycles (GBC) features research on regional to global biogeochemical interactions, as well as more local studies that demonstrate fundamental implications for biogeochemical processing at regional or global scales. Published papers draw on a wide array of methods and knowledge and extend in time from the deep geologic past to recent historical and potential future interactions. This broad scope includes studies that elucidate human activities as interactive components of biogeochemical cycles and physical Earth Systems including climate. Authors are required to make their work accessible to a broad interdisciplinary range of scientists.