China has the largest area of inland geological phosphorus-rich(GPR) mountains in the world, where vegetation restoration is key to safeguarding the environment. We reviewed the published literature and collected new ...China has the largest area of inland geological phosphorus-rich(GPR) mountains in the world, where vegetation restoration is key to safeguarding the environment. We reviewed the published literature and collected new data in order to analyze re-vegetation patterns and the status of plant communities in central Yunnan. The aim of our analysis was to suggest future improvements to restoration strategies in GPR mountain regions. Our results showed that spontaneous recovery was the most widespread type of restoration. N-fixing species such as Coriaria nepalensis and Alnus nepalensis play a vital role in succession. In the past, monoculture tree plantation was the primary method used in afforestation activities in central Yunnan; in recent years however, several different methods of restoration have been introduced including the use of agroforestry systems. For practical restoration, we found that spontaneous recovery was capable of delivering the best results, but that during its early stages, restoration results were affected by several factors including erosion risk, the origin of propagates and environmental variation. In contrast, methods employing human-made communities performed better in their early stages, but were constrained by higher costs and vulnerability to degradation and erosion. The use of N-fixing species such as A. nepalensis and Acacia mearnsii in plantations were unsuccessful in restoring full ecosystem functions. The success of restoration activities in GPR mountain regions could be improved through the following measures:(1) developing a better understanding of the respective advantages and disadvantages of current natural and human-engineered restoration approaches;(2) elucidating the feedback mechanism between phosphorus-rich soil and species selected for restoration, especially N-fixing species;(3) introducing market incentives aimed at encouraging specific restoration activities such as agroforestry, and improving the industry value chain.展开更多
The habitat structure and floristic composition examined <span style="font-family:Verdana;">for </span><span style="font-family:Verdana;">this study are of great importance, provi...The habitat structure and floristic composition examined <span style="font-family:Verdana;">for </span><span style="font-family:Verdana;">this study are of great importance, providing a scientific baseline of information for developing a biodiversity database and in supporting crucial information for the management decision-making process of the buffer zones. The primary objective of this study was to examine the current status of species composition and stand structure of moist evergreen forests distributed in the TNR buffer zone. Forest inventory was conducted in the primary moist evergreen forest (~1 ha) and secondary moist evergreen forest (~1 ha). In the TNR buffer zone, 83 species belonging to 31 families in the primary moist evergreen forest and 86 species belonging to 32 families in the secondary moist evergreen forest were found. The most dominant families in the primary moist evergreen forest were Dipterocarpaceae, Sapindaceae, Meliaceae, Myrtaceae, and Myristicaceae;at species level</span><span style="font-family:Verdana;">;</span><span style="font-family:;" "=""><span style="font-family:Verdana;">this forest was composed of </span><i><span style="font-family:Verdana;">Nephelium</span></i><span style="font-family:Verdana;"> <i>lappaceum</i></span><span style="font-family:Verdana;">, </span><i><span style="font-family:Verdana;">Myristica</span></i><span style="font-family:Verdana;"> <i>malabarica</i></span><span style="font-family:Verdana;">, </span><i><span style="font-family:Verdana;">Nephelium</span></i><span style="font-family:Verdana;"> <i>laurium</i></span><span style="font-family:Verdana;">, </span><i><span style="font-family:Verdana;">Aglaia</span></i><span style="font-family:Verdana;"> <i>andamanica</i></span><span style="font-family:Verdana;">, and </span><i><span style="font-family:Verdana;">Diospyros</span></i><span style="font-family:Verdana;"> <i>peregrine</i></span><span style="font-family:Verdana;">. The most dominant families in the secondary moist evergreen forest were Myrtaceae, Sapindaceae, Euphorbiaceae, Myristicaceae, and Lauraceae, while </span><i><span style="font-family:Verdana;">Nephelium</span></i><span style="font-family:Verdana;"> <i>lappaceum</i></span><span style="font-family:Verdana;">, </span><i><span style="font-family:Verdana;">Syzygium</span></i><span> <i><span style="font-family:Verdana;">claviflorum</span></i><span style="font-family:Verdana;">, </span><i><span style="font-family:Verdana;">Syzygium</span></i> </span><span style="font-family:Verdana;">sp-1</span><span><span style="font-family:Verdana;">, </span><i><span style="font-family:Verdana;">Eugenia</span></i> <i><span style="font-family:Verdana;">oblate</span></i></span><span style="font-family:Verdana;">, and </span><i><span style="font-family:Verdana;">Myristica</span></i><span style="font-family:Verdana;"> <i>angustifolia</i></span><span style="font-family:Verdana;"> were the most dominant at the species level. The results of S?rensen’s similarity index based on common species (Ks) and the similarity index based on species dominance (Kd) were observed at about 55% and 75% between the primary and secondary moist evergreen forests. The basal area (51.39 </span></span><span style="font-family:;" "=""><span style="font-family:Verdana;">m</span><sup><span style="font-family:Verdana;">2.</span></sup><span style="font-family:Verdana;">ha<sup>-</sup></span></span><span style="font-family:Verdana;"><sup>1</sup></span><span style="font-family:Verdana;">) of the primary moist evergreen forest was higher than that (44.50 </span><span style="font-family:;" "=""><span style="font-family:Verdana;">m</span><sup><span style="font-family:Verdana;">2</span></sup><span style="font-family:Verdana;"><sup>.</sup>ha<span style="font-size:10px;"><sup>-1</sup></span></span></span><span style="font-family:Verdana;">) of the secondary moist evergreen forest. Between these two forest types, the Shannon-Wiener, the Simpson and the Evenness indices were not significantly different at (p < 0.05). The total number of trees per hectare (n/ha) of the primary and secondary moist evergreen forests w</span><span style="font-family:Verdana;">ere</span><span style="font-family:Verdana;"> 910 (±184) and 991</span><span style="font-family:;" "=""> </span><span style="font-family:Verdana;">(±183).</span> <div class="__kindeditor_paste__" style="position:absolute;width:1px;height:1px;overflow:hidden;left:-1981px;top:202px;white-space:nowrap;"> <table border="1" width="100%" cellspacing="0" cellpadding="0" style="outline:0px;border-spacing:0px;width:772px;margin-bottom:0px;margin-left:auto;margin-right:auto;overflow-wrap:break-word;color:#333333;font-family:-apple-system, " font-size:14px;background-color:#ffffff;"=""> <tbody style="box-sizing:border-box;outline:0px;border:0px;overflow-wrap:break-word;"> <tr style="box-sizing:border-box;outline:0px;border-width:1px 0px 0px;border-right-style:initial;border-bottom-style:initial;border-left-style:initial;border-right-color:initial;border-bottom-color:initial;border-left-color:initial;border-image:initial;border-top-style:solid;border-top-color:#DDDDDD;overflow-wrap:break-word;"> <td style="box-sizing:border-box;outline:0px;padding:8px;margin:0px;overflow-wrap:break-word;border:1px solid #DDDDDD;font-size:14px;color:#4F4F4F;line-height:22px;"> <p align="left" style="box-sizing:border-box;outline:0px;margin-top:0px;margin-bottom:0px;padding:0px;overflow:auto hidden;line-height:22px;"> ? </p> </td> </tr> </tbody> </table> </div>展开更多
The objective of this study was to compare the soil seed bank in an area under natural regeneration(F1)and another reforested through seedling planting(F2),seven years after bauxite mining,in Southeast,Brazil.In each ...The objective of this study was to compare the soil seed bank in an area under natural regeneration(F1)and another reforested through seedling planting(F2),seven years after bauxite mining,in Southeast,Brazil.In each area,10 sampling points were randomly distributed,using three samples of topsoil to represent each point.The samples were transported to a shade house and evaluated for six months,where emerging individuals were identified every two weeks.Floristic similarity was evaluated with cluster analysis based on the Jaccard index(SJ).Species richness and abundance of individuals were compared using Student's t test.In F1,2,114.94 propagules m-2 were registered,belonging to 51 species and 24 botanical families,Shannon-Wiener diversity index H’=2.770 and Pielou evenness index J’=0.705.In F2,1,168.62 propagules m-2 were registered,belonging to 42 species and 22 families,H’=2.618 and J’=0.700.The(SJ)between F1 and F2 was 0.61,indicating a high similarity.The results showed high density of propagules,good diversity and absence of ecological dominance.The high number of individuals and diversity of tree species with zoochoric dispersion found in the areas indicates that both natural regeneration and reforestation were efficient in the ecological restoration of bauxite mined areas.展开更多
Aims Resistance distance(RD),based on circuit theory,is a promising metric for modelling effects of landscape configuration on dispersal of organ-isms and the resulting population and community patterns.The values of ...Aims Resistance distance(RD),based on circuit theory,is a promising metric for modelling effects of landscape configuration on dispersal of organ-isms and the resulting population and community patterns.The values of RD reflect the likelihood of a random walker to reach from a source to a certain destination in the landscape.Although it has successfully been used to model genetic structures of animal populations,where it most often outperforms other isolation metrics,there are hardly any applications to plants and,in particular,to plant community data.Our aims were to test if RD was a suitable metric for studying dispersal processes of plants in narrow habitat corridors(linear landscape ele-ments[LLE]).This would be the case,if dispersal processes(seed dis-persal and migration)resembled random walks.Further,we compared the model performance of RD against least-cost distance(LCD)and Euclidean distance(ED).Finally,we tested the suitability of different cost surfaces for calculations of LCD and RD.Methods We used data from 50 vegetation plots located on semi-natural LLE(field margins,ditches,road verges)in eight agricultural landscapes of Northwest Germany.We mapped LLE,including hedges and tree rows,from aerial images in a Geographic Information System,con-verted the maps into raster layers,and assigned resistance values to the raster cells,where all cells outside of LLE received infinite resist-ance and,thus,represented barriers to dispersal.For all pairs of plots within study areas,we calculated Jaccard similarity assuming that it was a proxy(or correlate)of dispersal events between plots.Further,we calculated RD and LCD of the network of LLE and ED between the plots.We modelled the effects of distance metrics on community similarity using binomial generalized linear mixed models.Important Findings ED was clearly the least suitable isolation metrics.Further,we found that RD performed better than LCD at modelling Jaccard similar-ity.Predictions varied markedly between the two distance metrics suggesting that RD comprises additional information about the landscape beyond spatial distance,such as the possible presence of multiple pathways between plots.Cost surfaces with equal cell-level resistances for all types of LLE performed better than more complex ones with habitat-specific resistances.We conclude that RD is a highly suitable measure of isolation or,inversely,connec-tivity for studying dispersal processes of plants within habitat cor-ridors.It is likely also suitable for assessing landscape permeability in other landscape types with areal habitats instead of narrow cor-ridors.RD holds the potential to improve assessments of isolation(or connectivity)for models of regional population and meta-com-munity dynamics.展开更多
Aims Understanding succession in tropical forest is an important aspect of vegetation science,but to date,successional processes in sea-sonally dry tropical forests(SDtFs)have received much less atten-tion than evergr...Aims Understanding succession in tropical forest is an important aspect of vegetation science,but to date,successional processes in sea-sonally dry tropical forests(SDtFs)have received much less atten-tion than evergreen humid tropical forests.We aim to fill this knowledge gap.Methods We investigated vegetation succession in SDtF areas consisting of three different successional stages(early,intermediate,late),and a SDtF-savanna ecotone in the municipal district of Juramento,north of Minas Gerais State,Brazil.Using twelve 400 m2 plots in each area,we compared vegetation parameters and structural variables(absolute density and basal area)and examined the floristic composition of the tree component to find gradients of change.Important Findings We found evidence of species turnover along a successional gradi-ent,with the intermediate stage showing the highest species rich-ness and diversity.this was accompanied with a significant increase in the number of tree individuals and basal area from the early to intermediate successional stage.However,the intermediate and late SDtF successional stages were more similar in structure and floristics.the ecotone was the most species rich and was similar to the intermediate SDtF and early successional stage in species richness and floristic composition respectively.these results will have implications for guiding SDtF management and recovery programs.展开更多
基金the support of the Chinese Academy of Sciences' Frontier Science Key Project (QYZDY-SSWSMC014)The Federal Ministry for Economic Cooperation and Development, Germany(#13.1432.7-001.00)Project funded by Yunnan Postdoctoral Science Foundation (Y732081261)
文摘China has the largest area of inland geological phosphorus-rich(GPR) mountains in the world, where vegetation restoration is key to safeguarding the environment. We reviewed the published literature and collected new data in order to analyze re-vegetation patterns and the status of plant communities in central Yunnan. The aim of our analysis was to suggest future improvements to restoration strategies in GPR mountain regions. Our results showed that spontaneous recovery was the most widespread type of restoration. N-fixing species such as Coriaria nepalensis and Alnus nepalensis play a vital role in succession. In the past, monoculture tree plantation was the primary method used in afforestation activities in central Yunnan; in recent years however, several different methods of restoration have been introduced including the use of agroforestry systems. For practical restoration, we found that spontaneous recovery was capable of delivering the best results, but that during its early stages, restoration results were affected by several factors including erosion risk, the origin of propagates and environmental variation. In contrast, methods employing human-made communities performed better in their early stages, but were constrained by higher costs and vulnerability to degradation and erosion. The use of N-fixing species such as A. nepalensis and Acacia mearnsii in plantations were unsuccessful in restoring full ecosystem functions. The success of restoration activities in GPR mountain regions could be improved through the following measures:(1) developing a better understanding of the respective advantages and disadvantages of current natural and human-engineered restoration approaches;(2) elucidating the feedback mechanism between phosphorus-rich soil and species selected for restoration, especially N-fixing species;(3) introducing market incentives aimed at encouraging specific restoration activities such as agroforestry, and improving the industry value chain.
文摘The habitat structure and floristic composition examined <span style="font-family:Verdana;">for </span><span style="font-family:Verdana;">this study are of great importance, providing a scientific baseline of information for developing a biodiversity database and in supporting crucial information for the management decision-making process of the buffer zones. The primary objective of this study was to examine the current status of species composition and stand structure of moist evergreen forests distributed in the TNR buffer zone. Forest inventory was conducted in the primary moist evergreen forest (~1 ha) and secondary moist evergreen forest (~1 ha). In the TNR buffer zone, 83 species belonging to 31 families in the primary moist evergreen forest and 86 species belonging to 32 families in the secondary moist evergreen forest were found. The most dominant families in the primary moist evergreen forest were Dipterocarpaceae, Sapindaceae, Meliaceae, Myrtaceae, and Myristicaceae;at species level</span><span style="font-family:Verdana;">;</span><span style="font-family:;" "=""><span style="font-family:Verdana;">this forest was composed of </span><i><span style="font-family:Verdana;">Nephelium</span></i><span style="font-family:Verdana;"> <i>lappaceum</i></span><span style="font-family:Verdana;">, </span><i><span style="font-family:Verdana;">Myristica</span></i><span style="font-family:Verdana;"> <i>malabarica</i></span><span style="font-family:Verdana;">, </span><i><span style="font-family:Verdana;">Nephelium</span></i><span style="font-family:Verdana;"> <i>laurium</i></span><span style="font-family:Verdana;">, </span><i><span style="font-family:Verdana;">Aglaia</span></i><span style="font-family:Verdana;"> <i>andamanica</i></span><span style="font-family:Verdana;">, and </span><i><span style="font-family:Verdana;">Diospyros</span></i><span style="font-family:Verdana;"> <i>peregrine</i></span><span style="font-family:Verdana;">. The most dominant families in the secondary moist evergreen forest were Myrtaceae, Sapindaceae, Euphorbiaceae, Myristicaceae, and Lauraceae, while </span><i><span style="font-family:Verdana;">Nephelium</span></i><span style="font-family:Verdana;"> <i>lappaceum</i></span><span style="font-family:Verdana;">, </span><i><span style="font-family:Verdana;">Syzygium</span></i><span> <i><span style="font-family:Verdana;">claviflorum</span></i><span style="font-family:Verdana;">, </span><i><span style="font-family:Verdana;">Syzygium</span></i> </span><span style="font-family:Verdana;">sp-1</span><span><span style="font-family:Verdana;">, </span><i><span style="font-family:Verdana;">Eugenia</span></i> <i><span style="font-family:Verdana;">oblate</span></i></span><span style="font-family:Verdana;">, and </span><i><span style="font-family:Verdana;">Myristica</span></i><span style="font-family:Verdana;"> <i>angustifolia</i></span><span style="font-family:Verdana;"> were the most dominant at the species level. The results of S?rensen’s similarity index based on common species (Ks) and the similarity index based on species dominance (Kd) were observed at about 55% and 75% between the primary and secondary moist evergreen forests. The basal area (51.39 </span></span><span style="font-family:;" "=""><span style="font-family:Verdana;">m</span><sup><span style="font-family:Verdana;">2.</span></sup><span style="font-family:Verdana;">ha<sup>-</sup></span></span><span style="font-family:Verdana;"><sup>1</sup></span><span style="font-family:Verdana;">) of the primary moist evergreen forest was higher than that (44.50 </span><span style="font-family:;" "=""><span style="font-family:Verdana;">m</span><sup><span style="font-family:Verdana;">2</span></sup><span style="font-family:Verdana;"><sup>.</sup>ha<span style="font-size:10px;"><sup>-1</sup></span></span></span><span style="font-family:Verdana;">) of the secondary moist evergreen forest. Between these two forest types, the Shannon-Wiener, the Simpson and the Evenness indices were not significantly different at (p < 0.05). The total number of trees per hectare (n/ha) of the primary and secondary moist evergreen forests w</span><span style="font-family:Verdana;">ere</span><span style="font-family:Verdana;"> 910 (±184) and 991</span><span style="font-family:;" "=""> </span><span style="font-family:Verdana;">(±183).</span> <div class="__kindeditor_paste__" style="position:absolute;width:1px;height:1px;overflow:hidden;left:-1981px;top:202px;white-space:nowrap;"> <table border="1" width="100%" cellspacing="0" cellpadding="0" style="outline:0px;border-spacing:0px;width:772px;margin-bottom:0px;margin-left:auto;margin-right:auto;overflow-wrap:break-word;color:#333333;font-family:-apple-system, " font-size:14px;background-color:#ffffff;"=""> <tbody style="box-sizing:border-box;outline:0px;border:0px;overflow-wrap:break-word;"> <tr style="box-sizing:border-box;outline:0px;border-width:1px 0px 0px;border-right-style:initial;border-bottom-style:initial;border-left-style:initial;border-right-color:initial;border-bottom-color:initial;border-left-color:initial;border-image:initial;border-top-style:solid;border-top-color:#DDDDDD;overflow-wrap:break-word;"> <td style="box-sizing:border-box;outline:0px;padding:8px;margin:0px;overflow-wrap:break-word;border:1px solid #DDDDDD;font-size:14px;color:#4F4F4F;line-height:22px;"> <p align="left" style="box-sizing:border-box;outline:0px;margin-top:0px;margin-bottom:0px;padding:0px;overflow:auto hidden;line-height:22px;"> ? </p> </td> </tr> </tbody> </table> </div>
基金To the CNPq,Fapemig and Capes by research fellowships for the authors and to the Companhia Brasileira de Alumínio for provided infrastructure and financial support for the project.
文摘The objective of this study was to compare the soil seed bank in an area under natural regeneration(F1)and another reforested through seedling planting(F2),seven years after bauxite mining,in Southeast,Brazil.In each area,10 sampling points were randomly distributed,using three samples of topsoil to represent each point.The samples were transported to a shade house and evaluated for six months,where emerging individuals were identified every two weeks.Floristic similarity was evaluated with cluster analysis based on the Jaccard index(SJ).Species richness and abundance of individuals were compared using Student's t test.In F1,2,114.94 propagules m-2 were registered,belonging to 51 species and 24 botanical families,Shannon-Wiener diversity index H’=2.770 and Pielou evenness index J’=0.705.In F2,1,168.62 propagules m-2 were registered,belonging to 42 species and 22 families,H’=2.618 and J’=0.700.The(SJ)between F1 and F2 was 0.61,indicating a high similarity.The results showed high density of propagules,good diversity and absence of ecological dominance.The high number of individuals and diversity of tree species with zoochoric dispersion found in the areas indicates that both natural regeneration and reforestation were efficient in the ecological restoration of bauxite mined areas.
文摘Aims Resistance distance(RD),based on circuit theory,is a promising metric for modelling effects of landscape configuration on dispersal of organ-isms and the resulting population and community patterns.The values of RD reflect the likelihood of a random walker to reach from a source to a certain destination in the landscape.Although it has successfully been used to model genetic structures of animal populations,where it most often outperforms other isolation metrics,there are hardly any applications to plants and,in particular,to plant community data.Our aims were to test if RD was a suitable metric for studying dispersal processes of plants in narrow habitat corridors(linear landscape ele-ments[LLE]).This would be the case,if dispersal processes(seed dis-persal and migration)resembled random walks.Further,we compared the model performance of RD against least-cost distance(LCD)and Euclidean distance(ED).Finally,we tested the suitability of different cost surfaces for calculations of LCD and RD.Methods We used data from 50 vegetation plots located on semi-natural LLE(field margins,ditches,road verges)in eight agricultural landscapes of Northwest Germany.We mapped LLE,including hedges and tree rows,from aerial images in a Geographic Information System,con-verted the maps into raster layers,and assigned resistance values to the raster cells,where all cells outside of LLE received infinite resist-ance and,thus,represented barriers to dispersal.For all pairs of plots within study areas,we calculated Jaccard similarity assuming that it was a proxy(or correlate)of dispersal events between plots.Further,we calculated RD and LCD of the network of LLE and ED between the plots.We modelled the effects of distance metrics on community similarity using binomial generalized linear mixed models.Important Findings ED was clearly the least suitable isolation metrics.Further,we found that RD performed better than LCD at modelling Jaccard similar-ity.Predictions varied markedly between the two distance metrics suggesting that RD comprises additional information about the landscape beyond spatial distance,such as the possible presence of multiple pathways between plots.Cost surfaces with equal cell-level resistances for all types of LLE performed better than more complex ones with habitat-specific resistances.We conclude that RD is a highly suitable measure of isolation or,inversely,connec-tivity for studying dispersal processes of plants within habitat cor-ridors.It is likely also suitable for assessing landscape permeability in other landscape types with areal habitats instead of narrow cor-ridors.RD holds the potential to improve assessments of isolation(or connectivity)for models of regional population and meta-com-munity dynamics.
文摘Aims Understanding succession in tropical forest is an important aspect of vegetation science,but to date,successional processes in sea-sonally dry tropical forests(SDtFs)have received much less atten-tion than evergreen humid tropical forests.We aim to fill this knowledge gap.Methods We investigated vegetation succession in SDtF areas consisting of three different successional stages(early,intermediate,late),and a SDtF-savanna ecotone in the municipal district of Juramento,north of Minas Gerais State,Brazil.Using twelve 400 m2 plots in each area,we compared vegetation parameters and structural variables(absolute density and basal area)and examined the floristic composition of the tree component to find gradients of change.Important Findings We found evidence of species turnover along a successional gradi-ent,with the intermediate stage showing the highest species rich-ness and diversity.this was accompanied with a significant increase in the number of tree individuals and basal area from the early to intermediate successional stage.However,the intermediate and late SDtF successional stages were more similar in structure and floristics.the ecotone was the most species rich and was similar to the intermediate SDtF and early successional stage in species richness and floristic composition respectively.these results will have implications for guiding SDtF management and recovery programs.