Gou Qian-qian , Zhao Wen-jia , Zhang Yan , Wang Guo-hua
{"title":"典型绿洲-荒漠交错带12年围篱后土壤性质和植物群落的变化","authors":"Gou Qian-qian , Zhao Wen-jia , Zhang Yan , Wang Guo-hua","doi":"10.1016/j.ecoleng.2025.107658","DOIUrl":null,"url":null,"abstract":"<div><div>Livestock grazing is the main cause of vegetation degradation and soil erosion in arid oasis–desert ecotones. Fencing has become the most important measure to promote the recovery of species diversity and plant community stabilization. In this study, we analyzed the changes in soil physical–chemical properties and plant diversity, niche width and overlap, inter-species associations, and community stability in a typical desert oasis ecotone of the Hexi Corridor in Northwest China following 12 years of continuous fencing. Available nutrients, particularly available nitrogen, increased significantly over the fencing period. However, no significant changes were observed in soil organic matter or total nitrogen. In the shrub layer, the dominant species shifted from <em>Nitraria sphaerocarpa</em> to a combination of <em>Nitraria sphaerocarpa</em> and <em>Reaumuria songarica</em> and then <em>Reaumuria songarica</em>. This shift was likely driven by greater nitrogen availability. In the herbaceous layer, the dominant species changed from <em>Zygophyllum mucronatum</em> and <em>Suaeda glauca</em> in the early stage (2–4 years) to <em>Artemisia scoparia</em> in the middle stage (5–8 years), and to <em>Eragrostis minor</em> in the late stage (9–10 years). The community diversity showed an increasing and then decreasing trend with 12 years of fencing. The niche overlap value for <em>Reaumuria songarica</em> was significantly higher than <em>Nitraria sphaerocarpa</em> from the sixth year. <em>Reaumuria songarica</em> became the keystone species after 12 years of fencing, and the recovery of <em>Reaumuria songarica</em> increased negative interspecific associations. These findings suggest that after 12 years of fencing, the soil and vegetation remain in a transitional phase, indicating that desert ecosystems require extended periods for full recovery.</div></div>","PeriodicalId":11490,"journal":{"name":"Ecological Engineering","volume":"217 ","pages":"Article 107658"},"PeriodicalIF":3.9000,"publicationDate":"2025-04-22","publicationTypes":"Journal Article","fieldsOfStudy":null,"isOpenAccess":false,"openAccessPdf":"","citationCount":"0","resultStr":"{\"title\":\"Changes in soil properties and plant community following twelve years of fencing in a typical oasis–desert ecotone\",\"authors\":\"Gou Qian-qian , Zhao Wen-jia , Zhang Yan , Wang Guo-hua\",\"doi\":\"10.1016/j.ecoleng.2025.107658\",\"DOIUrl\":null,\"url\":null,\"abstract\":\"<div><div>Livestock grazing is the main cause of vegetation degradation and soil erosion in arid oasis–desert ecotones. Fencing has become the most important measure to promote the recovery of species diversity and plant community stabilization. In this study, we analyzed the changes in soil physical–chemical properties and plant diversity, niche width and overlap, inter-species associations, and community stability in a typical desert oasis ecotone of the Hexi Corridor in Northwest China following 12 years of continuous fencing. Available nutrients, particularly available nitrogen, increased significantly over the fencing period. However, no significant changes were observed in soil organic matter or total nitrogen. In the shrub layer, the dominant species shifted from <em>Nitraria sphaerocarpa</em> to a combination of <em>Nitraria sphaerocarpa</em> and <em>Reaumuria songarica</em> and then <em>Reaumuria songarica</em>. This shift was likely driven by greater nitrogen availability. In the herbaceous layer, the dominant species changed from <em>Zygophyllum mucronatum</em> and <em>Suaeda glauca</em> in the early stage (2–4 years) to <em>Artemisia scoparia</em> in the middle stage (5–8 years), and to <em>Eragrostis minor</em> in the late stage (9–10 years). The community diversity showed an increasing and then decreasing trend with 12 years of fencing. The niche overlap value for <em>Reaumuria songarica</em> was significantly higher than <em>Nitraria sphaerocarpa</em> from the sixth year. <em>Reaumuria songarica</em> became the keystone species after 12 years of fencing, and the recovery of <em>Reaumuria songarica</em> increased negative interspecific associations. These findings suggest that after 12 years of fencing, the soil and vegetation remain in a transitional phase, indicating that desert ecosystems require extended periods for full recovery.</div></div>\",\"PeriodicalId\":11490,\"journal\":{\"name\":\"Ecological Engineering\",\"volume\":\"217 \",\"pages\":\"Article 107658\"},\"PeriodicalIF\":3.9000,\"publicationDate\":\"2025-04-22\",\"publicationTypes\":\"Journal Article\",\"fieldsOfStudy\":null,\"isOpenAccess\":false,\"openAccessPdf\":\"\",\"citationCount\":\"0\",\"resultStr\":null,\"platform\":\"Semanticscholar\",\"paperid\":null,\"PeriodicalName\":\"Ecological Engineering\",\"FirstCategoryId\":\"93\",\"ListUrlMain\":\"https://www.sciencedirect.com/science/article/pii/S0925857425001466\",\"RegionNum\":2,\"RegionCategory\":\"环境科学与生态学\",\"ArticlePicture\":[],\"TitleCN\":null,\"AbstractTextCN\":null,\"PMCID\":null,\"EPubDate\":\"\",\"PubModel\":\"\",\"JCR\":\"Q1\",\"JCRName\":\"ECOLOGY\",\"Score\":null,\"Total\":0}","platform":"Semanticscholar","paperid":null,"PeriodicalName":"Ecological Engineering","FirstCategoryId":"93","ListUrlMain":"https://www.sciencedirect.com/science/article/pii/S0925857425001466","RegionNum":2,"RegionCategory":"环境科学与生态学","ArticlePicture":[],"TitleCN":null,"AbstractTextCN":null,"PMCID":null,"EPubDate":"","PubModel":"","JCR":"Q1","JCRName":"ECOLOGY","Score":null,"Total":0}
Changes in soil properties and plant community following twelve years of fencing in a typical oasis–desert ecotone
Livestock grazing is the main cause of vegetation degradation and soil erosion in arid oasis–desert ecotones. Fencing has become the most important measure to promote the recovery of species diversity and plant community stabilization. In this study, we analyzed the changes in soil physical–chemical properties and plant diversity, niche width and overlap, inter-species associations, and community stability in a typical desert oasis ecotone of the Hexi Corridor in Northwest China following 12 years of continuous fencing. Available nutrients, particularly available nitrogen, increased significantly over the fencing period. However, no significant changes were observed in soil organic matter or total nitrogen. In the shrub layer, the dominant species shifted from Nitraria sphaerocarpa to a combination of Nitraria sphaerocarpa and Reaumuria songarica and then Reaumuria songarica. This shift was likely driven by greater nitrogen availability. In the herbaceous layer, the dominant species changed from Zygophyllum mucronatum and Suaeda glauca in the early stage (2–4 years) to Artemisia scoparia in the middle stage (5–8 years), and to Eragrostis minor in the late stage (9–10 years). The community diversity showed an increasing and then decreasing trend with 12 years of fencing. The niche overlap value for Reaumuria songarica was significantly higher than Nitraria sphaerocarpa from the sixth year. Reaumuria songarica became the keystone species after 12 years of fencing, and the recovery of Reaumuria songarica increased negative interspecific associations. These findings suggest that after 12 years of fencing, the soil and vegetation remain in a transitional phase, indicating that desert ecosystems require extended periods for full recovery.
期刊介绍:
Ecological engineering has been defined as the design of ecosystems for the mutual benefit of humans and nature. The journal is meant for ecologists who, because of their research interests or occupation, are involved in designing, monitoring, or restoring ecosystems, and can serve as a bridge between ecologists and engineers.
Specific topics covered in the journal include: habitat reconstruction; ecotechnology; synthetic ecology; bioengineering; restoration ecology; ecology conservation; ecosystem rehabilitation; stream and river restoration; reclamation ecology; non-renewable resource conservation. Descriptions of specific applications of ecological engineering are acceptable only when situated within context of adding novelty to current research and emphasizing ecosystem restoration. We do not accept purely descriptive reports on ecosystem structures (such as vegetation surveys), purely physical assessment of materials that can be used for ecological restoration, small-model studies carried out in the laboratory or greenhouse with artificial (waste)water or crop studies, or case studies on conventional wastewater treatment and eutrophication that do not offer an ecosystem restoration approach within the paper.