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7,849 results for “Conservancy”
Figure 9 from: Miu IV, Chisamera GB, Popescu VD, Iosif R, Nita A, Manolache S, Gavril VD, Cobzaru I, Rozylowicz L (2018) Conservation priorities for terrestrial mammals in Dobrogea Region, Romania. ZooKeys 792: 133-158. https://doi.org/10.3897/zookeys.792.25314
Figure 9 Priority conservation areas for mammal species listed in Annexes II and IV of the Habitats Directive within Natura 2000 sites of Dobrogea. Areas have been graded according to their priority rank, with highest priorities (top 20%) shown in red.
Figure 5 from: Liu D, Zhou Y, Yang K, Zhang X, Chen Y, Li C, Li H, Song Z (2018) Low genetic diversity in broodstocks of endangered Chinese sucker, Myxocyprinus asiaticus: implications for artificial propagation and conservation. ZooKeys 792: 117-132. https://doi.org/10.3897/zookeys.792.23785
Figure 5 Neighbor-joining trees of individuals in three Myxocyprinusasiaticus broodstocks based on mtDNA control region.
Figure 1 from: Liu D, Zhou Y, Yang K, Zhang X, Chen Y, Li C, Li H, Song Z (2018) Low genetic diversity in broodstocks of endangered Chinese sucker, Myxocyprinus asiaticus: implications for artificial propagation and conservation. ZooKeys 792: 117-132. https://doi.org/10.3897/zookeys.792.23785
Figure 1 Map of sampling sites for the three Myxocyprinusasiaticus broodstocks. Key: black triangle Pixian Base of Sichuan Fisheries Research Institute, China (PBS); black star Yinbin Base of Sichuan Fisheries Research Institute, China (YBS); black square Yibin Rare Aquatic Animal Research Institute, China (YRA); broken circle river range where the wild broodstocks source of YBS; broken rectangle river range where the wild broodstocks source of YRA.
Figure 6 from: Miu IV, Chisamera GB, Popescu VD, Iosif R, Nita A, Manolache S, Gavril VD, Cobzaru I, Rozylowicz L (2018) Conservation priorities for terrestrial mammals in Dobrogea Region, Romania. ZooKeys 792: 133-158. https://doi.org/10.3897/zookeys.792.25314
Figure 6 Mammal species richness of Dobrogea at 10 × 10 km. Grids with high richness partially overlap. 1 North Dobrogea Plateau 2 Danube Delta, and 3 Agighiolului Hills.
Figure 4 from: Miu IV, Chisamera GB, Popescu VD, Iosif R, Nita A, Manolache S, Gavril VD, Cobzaru I, Rozylowicz L (2018) Conservation priorities for terrestrial mammals in Dobrogea Region, Romania. ZooKeys 792: 133-158. https://doi.org/10.3897/zookeys.792.25314
Figure 4 Hotspots of sampling efforts within Dobrogea. The numbered statistically significant hot-spots are 1 Valu lui Traian Biological Research Station and Fântânița-Murfatlar 2 North Dobrogea Plateau 3 Letea Forest Natural Reserve in the Danube Delta.
Figure 3 from: Liu D, Zhou Y, Yang K, Zhang X, Chen Y, Li C, Li H, Song Z (2018) Low genetic diversity in broodstocks of endangered Chinese sucker, Myxocyprinus asiaticus: implications for artificial propagation and conservation. ZooKeys 792: 117-132. https://doi.org/10.3897/zookeys.792.23785
Figure 3 Median-joining network of the mtDNA control region haplotypes of Myxocyprinusasiaticus. The size of each circle indicates the frequency of the corresponding haplotype in the whole data set.
Figure 2 from: Miu IV, Chisamera GB, Popescu VD, Iosif R, Nita A, Manolache S, Gavril VD, Cobzaru I, Rozylowicz L (2018) Conservation priorities for terrestrial mammals in Dobrogea Region, Romania. ZooKeys 792: 133-158. https://doi.org/10.3897/zookeys.792.25314
Figure 2 Accumulation of mammals' occurrence records (blue) and the number of records per year (red) within Dobrogea Region, Romania.
Figure 10 from: Miu IV, Chisamera GB, Popescu VD, Iosif R, Nita A, Manolache S, Gavril VD, Cobzaru I, Rozylowicz L (2018) Conservation priorities for terrestrial mammals in Dobrogea Region, Romania. ZooKeys 792: 133-158. https://doi.org/10.3897/zookeys.792.25314
Figure 10 Zonation performance curves quantifying the proportion of remaining species occurrences covered by Natura 2000 sites in Dobrogea. When considering 20% of landscape within Natura 2000 sites as protected (e.g., conservation measures are enforced), 45% of Natura 2000 mammal occurrences are protected.
Figure 3 from: Miu IV, Chisamera GB, Popescu VD, Iosif R, Nita A, Manolache S, Gavril VD, Cobzaru I, Rozylowicz L (2018) Conservation priorities for terrestrial mammals in Dobrogea Region, Romania. ZooKeys 792: 133-158. https://doi.org/10.3897/zookeys.792.25314
Figure 3 Mammals reported occurrences in Dobrogea Region, Romania at 5 × 5 km resolution. Grids with reported occurrences before 1990 were plotted as old records whereas those with reported occurrences after 1990 were considered new records (reports of synanthropic and vagrant mammals were excluded).
Figure 2 from: Liu D, Zhou Y, Yang K, Zhang X, Chen Y, Li C, Li H, Song Z (2018) Low genetic diversity in broodstocks of endangered Chinese sucker, Myxocyprinus asiaticus: implications for artificial propagation and conservation. ZooKeys 792: 117-132. https://doi.org/10.3897/zookeys.792.23785
Figure 2 Neighbor-joining tree based on FST values of the mtDNA control region (a) and phylogenetic tree of mtDNA control region haplotypes in Myxocyprinusasiaticus reconstructed with Bayesian inference (b). Bayesian posterior probabilities and bootstrap values are shown at nodes of neighbor-joining tree and BI tree, respectively. The number behind each haplotype represents the number of individuals from different sampling locations.
Figure 4 from: Liu D, Zhou Y, Yang K, Zhang X, Chen Y, Li C, Li H, Song Z (2018) Low genetic diversity in broodstocks of endangered Chinese sucker, Myxocyprinus asiaticus: implications for artificial propagation and conservation. ZooKeys 792: 117-132. https://doi.org/10.3897/zookeys.792.23785
Figure 4 Results of STRUCTURE of Myxocyprinusasiaticus broodstocks based on K = 3. Each column represents one individual and the colors represent the probability membership coefficient of that individual for each genetic cluster.
Figure 1 from: Miu IV, Chisamera GB, Popescu VD, Iosif R, Nita A, Manolache S, Gavril VD, Cobzaru I, Rozylowicz L (2018) Conservation priorities for terrestrial mammals in Dobrogea Region, Romania. ZooKeys 792: 133-158. https://doi.org/10.3897/zookeys.792.25314
Figure 1 Flowchart of diversity analyses and spatial prioritisation of conservation of terrestrial mammals within Dobrogea Region, Romania.
Figure 1 from: Costa WJEN, Amorim PF, Mattos JLO (2018) Diversity and conservation of seasonal killifishes of the Hypsolebias fulminantis complex from a Caatinga semiarid upland plateau, São Francisco River basin, northeastern Brazil (Cyprinodontiformes, Aplocheilidae). Zoosystematics and Evolution 94(2): 495-504. https://doi.org/10.3897/zse.94.29718
Figure 1 Bayesian phylogeny used to delimit species endemic to the upper Carnaíba de Dentro River drainage, inferred by using sequences of the mitochondrial gene cytochrome b, 416 bp. Posterior probability values below 95% are not depicted; asterisk above nodes represents maximum value of posterior probability (100 %); numbers before species names are catalogue numbers for voucher specimens.
Figure 4 from: Costa WJEN, Amorim PF, Mattos JLO (2018) Diversity and conservation of seasonal killifishes of the Hypsolebias fulminantis complex from a Caatinga semiarid upland plateau, São Francisco River basin, northeastern Brazil (Cyprinodontiformes, Aplocheilidae). Zoosystematics and Evolution 94(2): 495-504. https://doi.org/10.3897/zse.94.29718
Figure 4 Geographical distribution of species of the Hypsolebias J'-clade in the upper Carnaíba de Dentro River drainage (yellow, H.fulminantis; red, H.splendissimus; black, H.carlettoi) and H.shibattai (white); stars indicate type localities.
Figure 2 from: Costa WJEN, Amorim PF, Mattos JLO (2018) Diversity and conservation of seasonal killifishes of the Hypsolebias fulminantis complex from a Caatinga semiarid upland plateau, São Francisco River basin, northeastern Brazil (Cyprinodontiformes, Aplocheilidae). Zoosystematics and Evolution 94(2): 495-504. https://doi.org/10.3897/zse.94.29718
Figure 2 Hypsolebiassplendissimus Costa sp. n., live holotype, UFRJ 6909, male, 42.7 mm SL. Photograph by W.J.E.M. Costa.
Figure 3 from: Costa WJEN, Amorim PF, Mattos JLO (2018) Diversity and conservation of seasonal killifishes of the Hypsolebias fulminantis complex from a Caatinga semiarid upland plateau, São Francisco River basin, northeastern Brazil (Cyprinodontiformes, Aplocheilidae). Zoosystematics and Evolution 94(2): 495-504. https://doi.org/10.3897/zse.94.29718
Figure 3 Hypsolebiassplendissimus Costa sp. n., live paratype, UFRJ 6779, female, 28.5 mm SL. Photograph by W.J.E.M. Costa.
Figure 3 from: Qin J, Liu X, Xu Y, Wu X, Ouyang S (2019) Beta diversity patterns of fish and conservation implications in the Luoxiao Mountains, China. ZooKeys 817: 73-93. https://doi.org/10.3897/zookeys.817.29337
Figure 3 Results of the principal component analysis (PCA) on the compositional similarity of fish species in the streams of the Luoxiao Mountains. JJ: Jinjiang River; YS: Yuanshui River; HS: Heshui River; SS: Shushui River; SC: Suichuan River; SY: Shangyou River; MS: Mishui River; ML: Miluo River; FS: Fushui River; XH: Xiuhe River; LY: Liuyang River.
Supplementary material 1 from: Dyderski MK, Jagodziński AM (2019) Functional traits of acquisitive invasive woody species differ from conservative invasive and native species. NeoBiota 41: 91-113. https://doi.org/10.3897/neobiota.41.31908
: Link: https://doi.org/10.3897/neobiota.41.31908.suppl1
Figure 4 from: Smith R (2019) The CLUZ plugin for QGIS: designing conservation area systems and other ecological networks. Research Ideas and Outcomes 5: e33510. https://doi.org/10.3897/rio.5.e33510
Figure 4 Screenshots from QGIS showing the two Marxan outputs displayed in CLUZ. The map on the left shows the best portfolio of planning units selected by Marxan, while the map on the right shows the selection frequency score of each planning unit based on running Marxan ten times, with planning units in red being selected in every one of the ten Marxan runs.
Figure 3 from: Smith R (2019) The CLUZ plugin for QGIS: designing conservation area systems and other ecological networks. Research Ideas and Outcomes 5: e33510. https://doi.org/10.3897/rio.5.e33510
Figure 3 Screenshot of QGIS showing the planning units layer, CLUZ target table and Change Status panel. The Change Status Panel was used to change the status of the patch of planning units in the northwest of the planning region from Conserved to Earmarked. This updated the target table, which shows that adding this new patch to the protected area network would meet the target for rock faces and would contribute towards targets for another five conservation features.
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