Composition, phenology and restoration of campo rupestre mountain grasslands - Brazil

Global environmental changes, especially land-use changes, have profound effects on both ecosystem functioning and biodiversity, having already altered many ecosystem services. These losses emphasize the need to preserve what remains; however when conservation programs are not sufficient, restoring...

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Main Author: Le Stradic, Soizig
Language:ENG
Published: Université d'Avignon 2012
Subjects:
Online Access:http://tel.archives-ouvertes.fr/tel-00942593
http://tel.archives-ouvertes.fr/docs/00/94/25/93/PDF/SLeStradic_PhD_finalbw.pdf
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spelling ndltd-CCSD-oai-tel.archives-ouvertes.fr-tel-009425932014-02-11T03:23:07Z http://tel.archives-ouvertes.fr/tel-00942593 2012AVIG0643 http://tel.archives-ouvertes.fr/docs/00/94/25/93/PDF/SLeStradic_PhD_finalbw.pdf Composition, phenology and restoration of campo rupestre mountain grasslands - Brazil Le Stradic, Soizig [SDV:SA] Life Sciences/Agricultural sciences [SDV:SA] Sciences du Vivant/Sciences agricoles Cerrado Community ecology Germination Grassland restoration Hay transfer Neotropical mountain ecosystems Restoration ecology Rupestrian fields Rupestrian grasslands Savannas Seed bank Translocation Transplantation Turf transfer Global environmental changes, especially land-use changes, have profound effects on both ecosystem functioning and biodiversity, having already altered many ecosystem services. These losses emphasize the need to preserve what remains; however when conservation programs are not sufficient, restoring areas that have been destroyed or disturbed can improve conservation efforts and mitigate damages. This work focuses on campos rupestres, Neotropical grasslands found at altitudes, which are part of the Cerrado (Brazilian savannas). They host a great biodiversity with a high level of endemism and, like other mountain ecosystems, provide valuable ecosystem services, such as water purification and recreational services. They have been and still are being impacted by human activities, such as civil engineering construction, quarrying or mining. The first objective of this thesis was to describe the reference ecosystem in order to aim for a clear restoration target and to monitor progress and success. We show that campos rupestres are composed of at least two distinct plant communities (i.e. sandy and stony grasslands), each having a specific composition and structure, hosting a great biodiversity. Several phenological patterns occur among the herbaceous communities: the majority of species flowers and fruits appear during the rainy season but other patterns can be observed. During our 2-year survey, some dominant species belonging to Poaceae, among others, were not observed reproducing, which implies limited chances to disperse on degraded areas. Campo rupestre vegetation is not resilient following a strong disturbance: several years after the disturbance, almost no native species are encountered on the degraded areas, soils are completely altered and seed bank recomposes only with non-target ruderal species. According to the filter model, a local community is a subset of the regional species pool determined by a set of dispersal, abiotic and biotic filters. Acting on the different filters to influence the plant community was the core of our restoration interventions. We then applied three in-situ restoration protocols (hay transfer, species translocation and turf translocation) to restore both kinds of grassland. Hay transfer does not allow the restoration of campo rupestre vegetation because of soil alteration and mainly because of poor seed quality. Indeed, germination studies show that, while some Xyridaceae and Velloziaceae have a high germinability, some dominant Poaceae, Cyperaceae or Asteraceae species have embryoless, unviable or dormant seeds, which makes seeding less efficient. There is no evidence that fire-related cues enhance germination in campos rupestres. Species translocation is successful for only one species, Paspalum erianthum; for the others, root damages probably impede survival. Finally, turf translocation is the most successful method, since numerous species are re-introduced on degraded areas. However due to the low resilience of pristine campos rupestres where turfs are taken from, turf translocation can only be considered in the case of habitat rescue, in circumstances when complete habitat destruction is otherwise unavoidable. Face to the difficulty to restore these peculiar grasslands, the protection and the conservation of campos rupestres must be made a high priority 2012-12-14 ENG PhD thesis Université d'Avignon
collection NDLTD
language ENG
sources NDLTD
topic [SDV:SA] Life Sciences/Agricultural sciences
[SDV:SA] Sciences du Vivant/Sciences agricoles
Cerrado
Community ecology
Germination
Grassland restoration
Hay transfer
Neotropical mountain ecosystems
Restoration ecology
Rupestrian fields
Rupestrian grasslands
Savannas
Seed bank
Translocation
Transplantation
Turf transfer
spellingShingle [SDV:SA] Life Sciences/Agricultural sciences
[SDV:SA] Sciences du Vivant/Sciences agricoles
Cerrado
Community ecology
Germination
Grassland restoration
Hay transfer
Neotropical mountain ecosystems
Restoration ecology
Rupestrian fields
Rupestrian grasslands
Savannas
Seed bank
Translocation
Transplantation
Turf transfer
Le Stradic, Soizig
Composition, phenology and restoration of campo rupestre mountain grasslands - Brazil
description Global environmental changes, especially land-use changes, have profound effects on both ecosystem functioning and biodiversity, having already altered many ecosystem services. These losses emphasize the need to preserve what remains; however when conservation programs are not sufficient, restoring areas that have been destroyed or disturbed can improve conservation efforts and mitigate damages. This work focuses on campos rupestres, Neotropical grasslands found at altitudes, which are part of the Cerrado (Brazilian savannas). They host a great biodiversity with a high level of endemism and, like other mountain ecosystems, provide valuable ecosystem services, such as water purification and recreational services. They have been and still are being impacted by human activities, such as civil engineering construction, quarrying or mining. The first objective of this thesis was to describe the reference ecosystem in order to aim for a clear restoration target and to monitor progress and success. We show that campos rupestres are composed of at least two distinct plant communities (i.e. sandy and stony grasslands), each having a specific composition and structure, hosting a great biodiversity. Several phenological patterns occur among the herbaceous communities: the majority of species flowers and fruits appear during the rainy season but other patterns can be observed. During our 2-year survey, some dominant species belonging to Poaceae, among others, were not observed reproducing, which implies limited chances to disperse on degraded areas. Campo rupestre vegetation is not resilient following a strong disturbance: several years after the disturbance, almost no native species are encountered on the degraded areas, soils are completely altered and seed bank recomposes only with non-target ruderal species. According to the filter model, a local community is a subset of the regional species pool determined by a set of dispersal, abiotic and biotic filters. Acting on the different filters to influence the plant community was the core of our restoration interventions. We then applied three in-situ restoration protocols (hay transfer, species translocation and turf translocation) to restore both kinds of grassland. Hay transfer does not allow the restoration of campo rupestre vegetation because of soil alteration and mainly because of poor seed quality. Indeed, germination studies show that, while some Xyridaceae and Velloziaceae have a high germinability, some dominant Poaceae, Cyperaceae or Asteraceae species have embryoless, unviable or dormant seeds, which makes seeding less efficient. There is no evidence that fire-related cues enhance germination in campos rupestres. Species translocation is successful for only one species, Paspalum erianthum; for the others, root damages probably impede survival. Finally, turf translocation is the most successful method, since numerous species are re-introduced on degraded areas. However due to the low resilience of pristine campos rupestres where turfs are taken from, turf translocation can only be considered in the case of habitat rescue, in circumstances when complete habitat destruction is otherwise unavoidable. Face to the difficulty to restore these peculiar grasslands, the protection and the conservation of campos rupestres must be made a high priority
author Le Stradic, Soizig
author_facet Le Stradic, Soizig
author_sort Le Stradic, Soizig
title Composition, phenology and restoration of campo rupestre mountain grasslands - Brazil
title_short Composition, phenology and restoration of campo rupestre mountain grasslands - Brazil
title_full Composition, phenology and restoration of campo rupestre mountain grasslands - Brazil
title_fullStr Composition, phenology and restoration of campo rupestre mountain grasslands - Brazil
title_full_unstemmed Composition, phenology and restoration of campo rupestre mountain grasslands - Brazil
title_sort composition, phenology and restoration of campo rupestre mountain grasslands - brazil
publisher Université d'Avignon
publishDate 2012
url http://tel.archives-ouvertes.fr/tel-00942593
http://tel.archives-ouvertes.fr/docs/00/94/25/93/PDF/SLeStradic_PhD_finalbw.pdf
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