We review achievements in the conservation of orchid diversity in China over the last 21 years.We provide updated information on orchid biodiversity and suggestions for orchid conservation in China.We outline national...We review achievements in the conservation of orchid diversity in China over the last 21 years.We provide updated information on orchid biodiversity and suggestions for orchid conservation in China.We outline national policies of biodiversity conservation,especially of orchid conservation,which provide general guidelines for orchid conservation in China.There are now approximately 1708 known species of Orchidaceae in 181 genera in China,including five new genera and 365 new species described over the last 21 years.The assessment of risk of extinction of all 1502 known native orchid species in China in 2013 indicated that 653 species were identified as threatened,132 species were treated as data-deficient,and four species endemic to China were classified as extinct.Approximately 1100 species(ca.65%)are protected in national nature reserves,and another~66 species in provincial nature reserves.About 800 native orchid species have living collections in major botanical gardens.The pollination biology of 74 native orchid species and the genetic diversity and spatial genetic structure of 29 orchid species have been investigated at a local scale and/or across species distributions.The mycorrhizal fungal community composition has been investigated in many genera,such as Bletilla,Coelogyne,Cymbidium,Cypripedium,and Dendrobium.Approximately 292 species will be included in the list of national key protected wild plants this year.Two major tasks for near future include in situ conservation and monitoring population dynamics of endangered species.展开更多
The Valencian Community(eastern Spain) was the pioneer territory establishing plant micro-reserves(PMRs). Its model to protect small sites for endemic and endangered plants has been exported to several countries aroun...The Valencian Community(eastern Spain) was the pioneer territory establishing plant micro-reserves(PMRs). Its model to protect small sites for endemic and endangered plants has been exported to several countries around the globe. This paper highlights 1) the role of PMRs to complement the protection provided by large protected areas, 2) how the establishment of PMRs fosters the increase of floristic knowledge, and 3)the fact that continuous monitoring of PMRs also yields new records of endangered species found within the same PMRs. The flexibility of the PMR approach-it can be adapted to other national and regional legislationsallows its transfer to other rich-biodiversity regions and countries such as China.展开更多
Rosa rugosa Thunb. is one of the dominant and important shrub species in estuary dunes and shingle beaches of northern China. However, its area of distribution, the number of populations, and the size of each populati...Rosa rugosa Thunb. is one of the dominant and important shrub species in estuary dunes and shingle beaches of northern China. However, its area of distribution, the number of populations, and the size of each population have decreased rapidly in the past two decades because of habitat degradation and loss. Random amplified polymorphic DNA markers were used to determine the genetic diversity of four remaining large natural populations of R. rugosa and to discuss an effective conservation strategy for this endangered species in China. High genetic variations were detected in R. rugosa populations in China. The mean percentage of polymorphic loci (P%) within four local populations was 57.99%, with the P% of the total population being 75.30%. Mean Shannon's information index (H0) was 0.2826, whereas total Ho was 0.3513. The genetic differentiation among populations was 0.1878, which indicates that most genetic diversity occurs within populations. Population Tumenjiang (TMJ) showed the highest genetic diversity (P% = 66.27%; H0 = 0.3117) and contained two exclusive bands. Population Changshandao (CSD) showed higher genetic diversity (P% =59.04%; H0 = 0.3065). Populations TMJ and CSD contained 95.33% and 99.33%, respectively, of loci with moderate to high frequency (P〉0.05) of the total population. These results indicate that populations TMJ and CSD should be given priority for in situ conservation and regarded as seed or propagule sources for ex situ conservation. The results of the present study also suggest that R. rugosa in China has become endangered as a result of human actions rather than genetic depression of populations; thus, human interference should be absolutely forbidden in R. rugosa habitats.展开更多
An online survey addressed to members listed in the European Cooperative Programme for Crop Genetic Resources Networks Working Group on Graithe current problems in the management of GL germplasm, to work out the crite...An online survey addressed to members listed in the European Cooperative Programme for Crop Genetic Resources Networks Working Group on Graithe current problems in the management of GL germplasm, to work out the criterian Legumes and Grain Legumes (GL) germplasm managers and breeders was carded out to pinpoint and decisions involved in the implementation of regeneration procedures and to identify strategic areas where further research is required. The survey was divided into three sections: (1) germplasm collection details and current status of the regeneration needs; (2) assessment over the understanding of basic information required to carry out appropriate regeneration procedures such as the breeding systems, the pollination requirements and pollinating agents, the isolation techniques and regeneration facilities; and (3) assessment of different options, in addition to "ex situ", such as "in situ" and "on farm" conservation. Obtaining, collating and analysing different kinds of existing data on mating system of GL species, effective pollination control methods and isolation facilities by species and location is one example of a priority issue. The GL community makes a clear request for greater support for the development of well-designed methodologies of regeneration that maintain the genetic structure of populations and that the optimum regeneration strategy is most likely to be achieved through integrating pollinators with the regeneration procedures. A major concern of the GL community is the lack of empirical scientific information on the most suitable pollinator agents.展开更多
In the management of UNESCO cultural sites of significant environmental importance, the erroneous assumption that the environment is independent of biological heritage often prevails. The mapping of phy</span>&l...In the management of UNESCO cultural sites of significant environmental importance, the erroneous assumption that the environment is independent of biological heritage often prevails. The mapping of phy</span><span style="font-family:Verdana;">l</span><span style="font-family:""><span style="font-family:Verdana;">ogenetic resources in the ancient city Matera-Sassi (MS) and the multivariable analysis at the level of ecotope and habitat have made it possible to identify the consistency of the plant genetic heritage and the biogenetic associations between the different ecotopes through the species they host. The bioclimatic variables and geomorphology of MS define an ecological niche refuge for rare or absent species in the surrounding landscape (e.g., </span><i><span style="font-family:Verdana;">Campanula</span></i><span style="font-family:Verdana;"> <i>versicolor</i></span><span style="font-family:Verdana;"> L., </span><i><span style="font-family:Verdana;">Centranthus</span></i><span style="font-family:Verdana;"> <i>ruber</i></span><span style="font-family:Verdana;"> (L.) Dc., </span><i><span style="font-family:Verdana;">Capparis</span></i> <i><span style="font-family:Verdana;">spinosa</span></i><span style="font-family:Verdana;"> L., </span><i><span style="font-family:Verdana;">Cymbalaria</span></i><span style="font-family:Verdana;"> <i>muralis</i></span><span style="font-family:Verdana;"> Hill, </span><i><span style="font-family:Verdana;">Crepis</span></i><span style="font-family:Verdana;"> spp., </span><i><span style="font-family:Verdana;">Lavathera</span></i><span style="font-family:Verdana;"> <i>arborea</i></span><span style="font-family:Verdana;"> L.) The total floristic capital in MS amounts to 190 species belonging to 59 different botanical families;80% are native species and only 4% are invasive. About half are Mediterranean with a moderate presence (17%) of cosmopolitan and sub-cosmopolitan;5% are endemic species. Autogenic ecotopes (Type I) represented by “Pleistocene limestone” and “House wall” contribute to the variation of total biodiversity through Endemic species mainly Chamephytes;anthropogenic ecotopes (Type III) such as “Garden” and “Town boundary” with Archaeophytes and exotic Neophytes mainly Phanerophytes;while “Humid margins” and mixed ecotope</span><span style="font-family:Verdana;">s (Type II) are linked to feral species and mainly to hemi-cr</span></span><span style="font-family:Verdana;">y</span><span style="font-family:Verdana;">ptophytes and therophytes. Minimum spanning tree of the habitat features</span><span style="font-family:Verdana;"> traced by the floristic biological heritage is consistent with the pedogenetic relationships between primary mother rocks, their derived ecotopes and anthropogenic impacts. Ecotope ranking based on its biodiversity value indicates that appropriate simultaneous conservation of both genetic resources and human works is achievable.展开更多
基金supported by Grants from National Forestry and Grassland Administration,China(No.2019073018,2019073019)National Natural Science Foundation of China(No.31870195,31670194)。
文摘We review achievements in the conservation of orchid diversity in China over the last 21 years.We provide updated information on orchid biodiversity and suggestions for orchid conservation in China.We outline national policies of biodiversity conservation,especially of orchid conservation,which provide general guidelines for orchid conservation in China.There are now approximately 1708 known species of Orchidaceae in 181 genera in China,including five new genera and 365 new species described over the last 21 years.The assessment of risk of extinction of all 1502 known native orchid species in China in 2013 indicated that 653 species were identified as threatened,132 species were treated as data-deficient,and four species endemic to China were classified as extinct.Approximately 1100 species(ca.65%)are protected in national nature reserves,and another~66 species in provincial nature reserves.About 800 native orchid species have living collections in major botanical gardens.The pollination biology of 74 native orchid species and the genetic diversity and spatial genetic structure of 29 orchid species have been investigated at a local scale and/or across species distributions.The mycorrhizal fungal community composition has been investigated in many genera,such as Bletilla,Coelogyne,Cymbidium,Cypripedium,and Dendrobium.Approximately 292 species will be included in the list of national key protected wild plants this year.Two major tasks for near future include in situ conservation and monitoring population dynamics of endangered species.
基金financial support from EU funds, including 2 LIFE-Nature projects and the EAFRD
文摘The Valencian Community(eastern Spain) was the pioneer territory establishing plant micro-reserves(PMRs). Its model to protect small sites for endemic and endangered plants has been exported to several countries around the globe. This paper highlights 1) the role of PMRs to complement the protection provided by large protected areas, 2) how the establishment of PMRs fosters the increase of floristic knowledge, and 3)the fact that continuous monitoring of PMRs also yields new records of endangered species found within the same PMRs. The flexibility of the PMR approach-it can be adapted to other national and regional legislationsallows its transfer to other rich-biodiversity regions and countries such as China.
基金supported financially by the Key Project of Natural Science Foundation of Shandong Province(No. Z2006D04)the Outstanding Young Scientists Foundation Grant of Shandong Province(No.2005 B S08010No.2006BS08008).
文摘Rosa rugosa Thunb. is one of the dominant and important shrub species in estuary dunes and shingle beaches of northern China. However, its area of distribution, the number of populations, and the size of each population have decreased rapidly in the past two decades because of habitat degradation and loss. Random amplified polymorphic DNA markers were used to determine the genetic diversity of four remaining large natural populations of R. rugosa and to discuss an effective conservation strategy for this endangered species in China. High genetic variations were detected in R. rugosa populations in China. The mean percentage of polymorphic loci (P%) within four local populations was 57.99%, with the P% of the total population being 75.30%. Mean Shannon's information index (H0) was 0.2826, whereas total Ho was 0.3513. The genetic differentiation among populations was 0.1878, which indicates that most genetic diversity occurs within populations. Population Tumenjiang (TMJ) showed the highest genetic diversity (P% = 66.27%; H0 = 0.3117) and contained two exclusive bands. Population Changshandao (CSD) showed higher genetic diversity (P% =59.04%; H0 = 0.3065). Populations TMJ and CSD contained 95.33% and 99.33%, respectively, of loci with moderate to high frequency (P〉0.05) of the total population. These results indicate that populations TMJ and CSD should be given priority for in situ conservation and regarded as seed or propagule sources for ex situ conservation. The results of the present study also suggest that R. rugosa in China has become endangered as a result of human actions rather than genetic depression of populations; thus, human interference should be absolutely forbidden in R. rugosa habitats.
文摘An online survey addressed to members listed in the European Cooperative Programme for Crop Genetic Resources Networks Working Group on Graithe current problems in the management of GL germplasm, to work out the criterian Legumes and Grain Legumes (GL) germplasm managers and breeders was carded out to pinpoint and decisions involved in the implementation of regeneration procedures and to identify strategic areas where further research is required. The survey was divided into three sections: (1) germplasm collection details and current status of the regeneration needs; (2) assessment over the understanding of basic information required to carry out appropriate regeneration procedures such as the breeding systems, the pollination requirements and pollinating agents, the isolation techniques and regeneration facilities; and (3) assessment of different options, in addition to "ex situ", such as "in situ" and "on farm" conservation. Obtaining, collating and analysing different kinds of existing data on mating system of GL species, effective pollination control methods and isolation facilities by species and location is one example of a priority issue. The GL community makes a clear request for greater support for the development of well-designed methodologies of regeneration that maintain the genetic structure of populations and that the optimum regeneration strategy is most likely to be achieved through integrating pollinators with the regeneration procedures. A major concern of the GL community is the lack of empirical scientific information on the most suitable pollinator agents.
文摘In the management of UNESCO cultural sites of significant environmental importance, the erroneous assumption that the environment is independent of biological heritage often prevails. The mapping of phy</span><span style="font-family:Verdana;">l</span><span style="font-family:""><span style="font-family:Verdana;">ogenetic resources in the ancient city Matera-Sassi (MS) and the multivariable analysis at the level of ecotope and habitat have made it possible to identify the consistency of the plant genetic heritage and the biogenetic associations between the different ecotopes through the species they host. The bioclimatic variables and geomorphology of MS define an ecological niche refuge for rare or absent species in the surrounding landscape (e.g., </span><i><span style="font-family:Verdana;">Campanula</span></i><span style="font-family:Verdana;"> <i>versicolor</i></span><span style="font-family:Verdana;"> L., </span><i><span style="font-family:Verdana;">Centranthus</span></i><span style="font-family:Verdana;"> <i>ruber</i></span><span style="font-family:Verdana;"> (L.) Dc., </span><i><span style="font-family:Verdana;">Capparis</span></i> <i><span style="font-family:Verdana;">spinosa</span></i><span style="font-family:Verdana;"> L., </span><i><span style="font-family:Verdana;">Cymbalaria</span></i><span style="font-family:Verdana;"> <i>muralis</i></span><span style="font-family:Verdana;"> Hill, </span><i><span style="font-family:Verdana;">Crepis</span></i><span style="font-family:Verdana;"> spp., </span><i><span style="font-family:Verdana;">Lavathera</span></i><span style="font-family:Verdana;"> <i>arborea</i></span><span style="font-family:Verdana;"> L.) The total floristic capital in MS amounts to 190 species belonging to 59 different botanical families;80% are native species and only 4% are invasive. About half are Mediterranean with a moderate presence (17%) of cosmopolitan and sub-cosmopolitan;5% are endemic species. Autogenic ecotopes (Type I) represented by “Pleistocene limestone” and “House wall” contribute to the variation of total biodiversity through Endemic species mainly Chamephytes;anthropogenic ecotopes (Type III) such as “Garden” and “Town boundary” with Archaeophytes and exotic Neophytes mainly Phanerophytes;while “Humid margins” and mixed ecotope</span><span style="font-family:Verdana;">s (Type II) are linked to feral species and mainly to hemi-cr</span></span><span style="font-family:Verdana;">y</span><span style="font-family:Verdana;">ptophytes and therophytes. Minimum spanning tree of the habitat features</span><span style="font-family:Verdana;"> traced by the floristic biological heritage is consistent with the pedogenetic relationships between primary mother rocks, their derived ecotopes and anthropogenic impacts. Ecotope ranking based on its biodiversity value indicates that appropriate simultaneous conservation of both genetic resources and human works is achievable.