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Soil resistance and recovery during neotropical forest succession

时序 生态演替 环境科学 抗性(生态学) 土壤肥力 土壤水分 森林砍伐(计算机科学) 次生演替 生态系统 土壤退化 植被(病理学) 森林恢复 农林复合经营 土壤碳 农学 森林生态学 生态学 土壤科学 生物 计算机科学 医学 病理 程序设计语言
作者
Masha T. van der Sande,Jennifer S. Powers,Thomas W. Kuyper,Natalia Norden,Beatriz Salgado‐Negret,Jarcilene Silva de Almeida‐Cortez,Frans Bongers,Diego Delgado,Daisy H. Dent,Géraldine Derroire,Mário Marcos do Espírito Santo,Juan Manuel Dupuy,G. Wilson Fernándes,Bryan Finegan,Mayra E. Gavito,José Luis Hernández‐Stefanoni,Catarina C. Jakovac,Isabel L. Jones,Maria das Dores Magalhães Veloso,Jorge A. Meave,Francisco Mora,Rodrigo Muñoz,Nathalia Pérez-Cárdenas,Daniel Piotto,Esteban Álvarez-Dávila,Yasmani Cáceres‐Siani,Coralie Dalban-Pilon,Aurélie Dourdain,Dan V. Du,Daniel García Villalobos,Yule Roberta Ferreira Nunes,Arturo Sánchez‐Azofeifa,Lourens Poorter
出处
期刊:Philosophical Transactions of the Royal Society B [The Royal Society]
卷期号:378 (1867) 被引量:13
标识
DOI:10.1098/rstb.2021.0074
摘要

The recovery of soil conditions is crucial for successful ecosystem restoration and, hence, for achieving the goals of the UN Decade on Ecosystem Restoration. Here, we assess how soils resist forest conversion and agricultural land use, and how soils recover during subsequent tropical forest succession on abandoned agricultural fields. Our overarching question is how soil resistance and recovery depend on local conditions such as climate, soil type and land-use history. For 300 plots in 21 sites across the Neotropics, we used a chronosequence approach in which we sampled soils from two depths in old-growth forests, agricultural fields (i.e. crop fields and pastures), and secondary forests that differ in age (1–95 years) since abandonment. We measured six soil properties using a standardized sampling design and laboratory analyses. Soil resistance strongly depended on local conditions. Croplands and sites on high-activity clay (i.e. high fertility) show strong increases in bulk density and decreases in pH, carbon (C) and nitrogen (N) during deforestation and subsequent agricultural use. Resistance is lower in such sites probably because of a sharp decline in fine root biomass in croplands in the upper soil layers, and a decline in litter input from formerly productive old-growth forest (on high-activity clays). Soil recovery also strongly depended on local conditions. During forest succession, high-activity clays and croplands decreased most strongly in bulk density and increased in C and N, possibly because of strongly compacted soils with low C and N after cropland abandonment, and because of rapid vegetation recovery in high-activity clays leading to greater fine root growth and litter input. Furthermore, sites at low precipitation decreased in pH, whereas sites at high precipitation increased in N and decreased in C : N ratio. Extractable phosphorus (P) did not recover during succession, suggesting increased P limitation as forests age. These results indicate that no single solution exists for effective soil restoration and that local site conditions should determine the restoration strategies. This article is part of the theme issue ‘Understanding forest landscape restoration: reinforcing scientific foundations for the UN Decade on Ecosystem Restoration’.
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