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125 results for “old growth”
X-ray imaging of 30 year old wine grape wood reveals cumulative impacts of rootstocks on scion secondary growth and harvest index
<p><span></span></p> <p><span>Annual rings from vines in a 30 year old, California rootstock trial were measured to determine the effects of 15 different rootstocks on Chardonnay and Cabernet Sauvignon scions. Viticultural traits measuring vegetative growth, yield, berry quality, and nutrient uptake were measured at the beginning and end of the lifetime of the vineyard.</span></p> <p><span>X-ray Computed Tomography (CT) was used to measure ring widths in 103 vines. Ring width was modeled as a function of ring number using a negative exponential model. Early and late wood ring widths, cambium width, and scion trunk radius were correlated with 27 traits. </span></p> <p><span>Modeling of annual ring width shows that scions alter the width of the first rings but that rootstocks alter the decay thereafter, consistently shortening ring width throughout the lifetime of the vine. The ratio of yield to vegetative growth, juice pH, photosynthetic assimilation and transpiration rates, and stomatal conductance are correlated with scion trunk radius.</span></p> <p><span>Rootstocks modulate secondary growth over years, altering hydraulic conductance, physiology, and agronomic traits. Rootstocks act in similar but distinct ways from climate to modulate ring width, which borrowing techniques from dendrochronology, can be used to monitor both genetic and environmental effects in woody perennial crop species.</span></p>
Figure 7 in Application Of Lichen Functional Traits In Identification Of Temperate Old-Growth Broad-Leaved Forests
Figure 7. Lichen thallus color in old (oldgrowth), middle (middleaged) and young broadleaved forest stands.
Figure 6 in Application Of Lichen Functional Traits In Identification Of Temperate Old-Growth Broad-Leaved Forests
Figure 6. Lichen growth forms in old (oldgrowth), middle (middleaged) and young broadleaved forest stands.
Figure 9 in Application Of Lichen Functional Traits In Identification Of Temperate Old-Growth Broad-Leaved Forests
Figure 9. Lichen photobiont type in old (oldgrowth), middle (middleaged) and young broadleaved forest stands.
Figure 8 in Application Of Lichen Functional Traits In Identification Of Temperate Old-Growth Broad-Leaved Forests
Figure 8. Lichen reproduction type in old (oldgrowth), middle (middleaged) and young broadleaved forest stands.
Figure 2 in Application Of Lichen Functional Traits In Identification Of Temperate Old-Growth Broad-Leaved Forests
Figure 2. Sample plot. Abbreviations: S – South, N – North. Arrow shows the direction of the sampling in transect. Tree number shows the order of surveyed trees.
Figure 5 in Application Of Lichen Functional Traits In Identification Of Temperate Old-Growth Broad-Leaved Forests
Figure 5. Number of lichen taxa with category of conservation concern in old (oldgrowth), middle (middleaged) and young broadleaved forest stands.
Data from: Vegetation dynamics 1946–2018 in an old-growth conifer forest
<p>We analysed ground vegetation in 250 plots in 2018 in the old-growth <em>Picea abies-</em>dominated<em> </em>forest Säby Västerskog, SE Sweden as a follow-up of studies in 1946 and 1998 with the same layout of plots. The vegetation changes were not clearly directional: the species composition in 2018 was intermediate between that of 1946 and 1998, whereas in 1998 species richness was higher and with the unique presence of a number of species indicating small-scale disturbances. <em>Vaccinium myrtillus</em> increased in cover since 1946 and <em>Avenella flexuosa</em> decreased. This goes against regional trends, attributed to climate warming and changes in nitrogen deposition. Regional changes are overshadowed by fine-scale disturbances and micro-successions.</p>
Large uptake of atmospheric OCS observed at a moist old growth forest: Controls and implications for carbon cycle applications
<p>This repository contains all data for the manuscript by Rastogi et al., titled "<strong>Large uptake of atmospheric OCS observed at a moist old growth forest: Controls and implications for carbon cycle applications</strong>". This manuscript has been accepted for publication in the Journal of Geophysical Research: Biogeosciences</p> <p> </p>
Community-weighted mean traits in old-growth and selectively logged forest
<p><strong>Description: </strong></p> <p>Community-weighted mean traits from tree species that make up more than 80% basal area in plots in selectively logged forest at SAFE and in old-growth forest in Danum Valley and Maliau Basin. Sampled during the BALI project traits campaign</p> <p><strong>Project: </strong>This dataset was collected as part of the following SAFE research project: <a href="https://www.safeproject.net/projects/project_view/55"><strong>Biodiversity and land-use impacts on tropical ecosystem function (BALI): Quantifying functional trait distributions across the disturbance gradient</strong></a></p> <p><strong>Funding: </strong>These data were collected as part of research funded by:</p> <ul> <li>NERC (Standard grant, NE/K016253/1)</li> </ul> <p>This dataset is released under the CC-BY 4.0 licence, requiring that you cite the dataset in any outputs, but has the additional condition that you acknowledge the contribution of these funders in any outputs.</p> <p> </p> <p><strong>Permits: </strong>These data were collected under permit from the following authorities:</p> <ul> <li>Sabah Biodiversity Centre (Research licence JKM/MBS.1000-2.2(385))</li> </ul> <p> </p> <p><strong>XML metadata: </strong>GEMINI compliant metadata for this dataset is available <a href="https://www.safeproject.net/datasets/xml_metadata?id=3247602">here</a></p> <p><strong>Files: </strong>This dataset consists of 3 files: Both_CWM_traits.xlsx, CSP_protocol_Chlorophyll_and_Carotenoids.pdf, CSP_protocol_Phenols_Tannins_Analysis.pdf</p> <p><strong>Both_CWM_traits.xlsx</strong></p> <p>This file contains dataset metadata and 1 data tables:</p> <ol> <li> <p><strong>CMW_traits</strong> (described in worksheet CMW_traits)</p> <p>Description: Community-weighted mean traits of tree in plots in SAFE , Danum Valley and Maliau Basin sampled during the BALI project traits campaign</p> <p>Number of fields: 36</p> <p>Number of data rows: 8</p> <p>Fields:</p> <ul> <li><strong>location</strong>: Location (Field type: Categorical)</li> <li><strong>forest_type</strong>: Forest type (Field type: Categorical)</li> <li><strong>forestplots_name</strong>: Plot name coherent with forestplots database (Field type: ID)</li> <li><strong>plot_name_trait_campaign</strong>: Plot name used during the BALI trait campaign (Field type: ID)</li> <li><strong>CWM_total_K_mg.g_log</strong>: CWM foliar potassium concentration in mg per g dry weight, log transformed data (Field type: Numeric)</li> <li><strong>CWM_total_Ca_mg.g_log</strong>: CWM foliar calcium concentration in mg per g dry weight, log transformed data (Field type: Numeric)</li> <li><strong>CWM_total_Mg_mg.g_log</strong>: CWM foliar magnesium concentration in mg per g dry weight, log transformed data (Field type: Numeric)</li> <li><strong>CWM_total_P_mg.g_log</strong>: CWM foliar phosporus concentration in mg per g dry weight, log transformed data (Field type: Numeric)</li> <li><strong>CWM_N_perc</strong>: CWM foliar nitrogen concentration (Field type: Numeric)</li> <li><strong>CWM_15N_per_mil</strong>: CWM foliar 15N isotope concentration (Field type: Numeric)</li> <li><strong>CWM_C_perc</strong>: CWM foliar carbon concentration (Field type: Numeric)</li> <li><strong>CWM_13C_per_mil</strong>: CWM foliar 13C isotope concentration, expressed relative to Vienna Pee Dee Belemnite (VPDB) as δ13C in units of per mil [‰] (Field type: Numeric)</li> <li><strong>CWM_DR</strong>: CWM dark respiration measured on leaf attached to a branch that is cut under water and remains in water (Field type: Numeric)</li> <li><strong>CWM_Asat</strong>: CWM light-saturated net photosynthesis measured on leaf attached to a branch that is cut under water and remains in water. (Field type: Numeric)</li> <li><strong>CWM_Amax</strong>: CWM maximum photosynthetic capacity measured on leaf attached to a branch that is cut under water and remains in water. (Field type: Numeric)</li> <li><strong>CWM_leaf_thickness_mm_log</strong>: CWM thickness of leaf, log transformed data (Field type: Numeric)</li> <li><strong>CWM_dry_weight_mg_log</strong>: CWM leaf oven-dried weight, log transformed data (Field type: Numeric)</li> <li><strong>CWM_LA_mm2_log</strong>: CWM leaf area (LA) calculated from fresh leaves collected from branches, scanned immediately, log transformed data (Field type: Numeric)</li> <li><strong>CWM_SLA_mm2_mg</strong>: CWM specific leaf area (SLA) determined as the one-sided area of a fresh leaf, divided by its oven-dry mass. (Field type: Numeric)</li> <li><strong>CWM_LDMC_mg.g</strong>: CWM leaf dry-matter content (LDMC) is the oven-dry mass (mg) of a leaf, divided by its water-saturated fresh mass (g) mg g–1 (Field type: Numeric)</li> <li><strong>CWM_chla_mg.g</strong>: CWM foliar chlorophyll a content (Field type: Numeric)</li> <li><strong>CWM_chlb_mg.g</strong>: CWM foliar chlorophyll b content (Field type: Numeric)</li> <li><strong>CWM_carot_mg.g</strong>: CWM foliar carotenoids content (Field type: Numeric)</li> <li><strong>CWM_Fp_N_mm_log</strong>: CWM force to punch leaf, dividing the observed force (N) required to puncture the leaf lamina by the circumference of the instrument's rod, log transformed data (Field type: Numeric)</li> <li><strong>CWM_specific_Fp_log</strong>: CWM specific force to punch (Fp divided by lamina thickness), log transformed data (Field type: Numeric)</li> <li><strong>CWM_WD_B</strong>: CWM branch wood density from branch segment with bark (Field type: Numeric)</li> <li><strong>CWM_hemicellulose_perc</strong>: CWM foliar hemicellulose concentration (Field type: Numeric)</li> <li><strong>CWM_cellulose_perc</strong>: CWM foliar cellulose concentration (Field type: Numeric)</li> <li><strong>CWM_lignin_recalcitrants_perc</strong>: CWM foliar lignin and recalcitrants concentration (Field type: Numeric)</li> <li><strong>CWM_total_tannin_mg.g</strong>: CWM foliar tannin concentration (Field type: Numeric)</li> <li><strong>CWM_total_phenol_mg.g</strong>: CWM total foliar phenol concentration (Field type: Numeric)</li> <li><strong>CWM_chla_mg.mm2</strong>: CWM foliar chlorophyll a content expressed on leaf area basis (Field type: Numeric)</li> <li><strong>CWM_chlb_mg.mm2</strong>: CWM foliar chlorophyll b content expressed on leaf area basis (Field type: Numeric)</li> <li><strong>CWM_carot_mg.mm2</strong>: CWM foliar carotenoids content expressed on leaf area basis (Field type: Numeric)</li> <li><strong>CWM_N_mg.mm2</strong>: CWM foliar nitrogen concentration expressed on leaf area basis (Field type: Numeric)</li> <li><strong>CWM_total_P_mg.mm2.l</strong>: CWM foliar phosporus concentration expressed on leaf area basis, log transformed data (Field type: Numeric)</li> </ul> </li> </ol> <p><strong>CSP_protocol_Chlorophyll_and_Carotenoids.pdf</strong></p> <p>Description: Methodology of chlorophyll and carotenoids analysis, Carnegie Spectranomics protocol: https://drive.google.com/file/d/0B58dyv8L3FpMdGw0QWtiZElHQzQ/view</p> <p><strong>CSP_protocol_Phenols_Tannins_Analysis.pdf</strong></p> <p>Description: Methodology of phenols and tannins analysis, Carnegie Spectranomics protocol: https://drive.google.com/file/d/0B58dyv8L3FpMcTBHblQwRHdyRE0/view</p> <p><strong>Date range: </strong>2014-05-01 to 2018-09-01</p> <p><strong>Latitudinal extent: </strong>4.5000 to 5.0700</p> <p><strong>Longitudinal extent: </strong>116.7500 to 117.8200</p>
Functional traits of tree species in old-growth and selectively logged forest
<b>Description: </b><p>Traits matrix for tree species in selectively logged forest at SAFE and in old-growth forest in Danum Valley and Maliau Basin. Sampled during the BALI project traits campaign</p><p><b>Project: </b>This dataset was collected as part of the following SAFE research project: <a href="https://www.safeproject.net/projects/project_view/55"><b>Biodiversity and land-use impacts on tropical ecosystem function (BALI): Quantifying functional trait distributions across the disturbance gradient</b></a></p><p><b>Funding: </b>These data were collected as part of research funded by: </p><ul><li>NERC (Standard grant, NE/K016253/1)</li></ul><p>This dataset is released under the CC-BY 4.0 licence, requiring that you cite the dataset in any outputs, but has the additional condition that you acknowledge the contribution of these funders in any outputs.</p><p></p><p><b>Permits: </b>These data were collected under permit from the following authorities:</p><ul><li>Sabah Biodiversity Centre (Research licence JKM/MBS.1000-2.2(385))</li></ul><p></p><p><b>XML metadata: </b>GEMINI compliant metadata for this dataset is available <a href="https://www.safeproject.net/datasets/xml_metadata?id=3247631">here</a></p><p><b>Files: </b>This dataset consists of 3 files: Both_tree_functional_traits.xlsx, CSP_protocol_Chlorophyll_and_Carotenoids.pdf, CSP_protocol_Phenols_Tannins_Analysis.pdf</p><p><b>Both_tree_functional_traits.xlsx</b></p><p>This file contains dataset metadata and 1 data tables:</p><ol><li><p><b>Tree_functional_traits</b> (described in worksheet Tree_functional_traits)</p><p>Description: Traits matrix for tree species at SAFE and in Danum Valley, Maliau Basin sampled during the BALI project traits campaign</p><p>Number of fields: 84</p><p>Number of data rows: 717</p><p>Fields: </p><ul><li><b>location</b>: Location (Field type: Categorical)</li><li><b>forest_type</b>: Forest type: OG: old-growth plots, Maliau and Danum; SL: selectively logged plots at SAFE (Field type: Categorical)</li><li><b>forestplots_name</b>: Plot name coherent with forestplots database (Field type: ID)</li><li><b>plot_name_trait_campaign</b>: Plot name used during the BALI trait campaign (Field type: ID)</li><li><b>sample_code</b>: Sample code referencing: plot-'T'(ree) ID-branch type (Field type: ID)</li><li><b>branch_type</b>: Binary classification of branch sampled depending on their position in the tree crown. BS: sun branch; BSH: shade branch (Field type: ID)</li><li><b>sampling_date</b>: Date of sampling (Field type: Date)</li><li><b>tree_id</b>: Reference for tree tag label (Field type: ID)</li><li><b>species</b>: Tree species (Field type: Taxa)</li><li><b>height.m</b>: Height of tree individual (Field type: Numeric trait)</li><li><b>total_K_mg.g</b>: Foliar potassium content in mg per g dry weight (Field type: Numeric trait)</li><li><b>total_Ca_mg.g</b>: Foliar calcium content in mg per g dry weight (Field type: Numeric trait)</li><li><b>total_Mg_mg.g</b>: Foliar magnesium content in mg per g dry weight (Field type: Numeric trait)</li><li><b>total_P_mg.g</b>: Foliar phosporus content in mg per g dry weight (Field type: Numeric trait)</li><li><b>N_perc</b>: Foliar nitrogen concentration (Field type: Numeric trait)</li><li><b>15N_per_mil</b>: Foliar 15N isotope concentration (Field type: Numeric trait)</li><li><b>C_perc</b>: Foliar carbon concentration (Field type: Numeric trait)</li><li><b>13C_per_mil</b>: Foliar 13C isotope concentration, expressed relative to Vienna Pee Dee Belemnite (VPDB) as δ13C in units of per mil [‰] (Field type: Numeric trait)</li><li><b>CN</b>: Foliar carbon nitrogen ratio (Field type: Numeric trait)</li><li><b>DR_mean</b>: Mean dark respiration measured on leaf of a branch that is cut under water and remains in water, calculated from replicated leaves per branch (Field type: Numeric trait)</li><li><b>DR_sd</b>: Standard deviation of dark respiration measured on leaf of a branch that is cut under water and remains in water, calculated from replicated leaves per branch (Field type: Numeric)</li><li><b>DR_n</b>: Number of replicates, i.e. leaves per branch used for mean trait (Field type: Replicate)</li><li><b>Asat_cons_mean</b>: Mean light-saturated net photosynthesis measured on leaf of a branch that is cut under water and remains in water, calculated from replicated leaves per branch. Data cleaning very conservative: subset of values only with conductance higher 0.04, Ci between 150 - 300, and PS higher than 1, leading to fewer data points. (Field type: Numeric trait)</li><li><b>Asat_cons_sd</b>: Standard deviation of light-saturated net photosynthesis measured on leaf of a branch that is cut under water and remains in water, calculated from replicated leaves per branch (Field type: Numeric)</li><li><b>Asat_cons_n</b>: Number of replicates, i.e. leaves per branch used for mean trait (Field type: Replicate)</li><li><b>Amax_cons_mean</b>: Mean maximum photosynthetic capacity measured on leaf of a branch that is cut under water and remains in water, calculated from replicated leaves per branch. Data cleaning very conservative: subset of values only with conductance higher 0.04, Ci between 150 - 300, and PS higher than 1, leading to fewer data points. (Field type: Numeric trait)</li><li><b>Amax_cons_sd</b>: Standard deviation of maximum photosynthetic capacity measured on leaf of a branch that is cut under water and remains in water, calculated from replicated leaves per branch (Field type: Numeric)</li><li><b>Amax_cons_n</b>: Number of replicates, i.e. leaves per branch used for mean trait (Field type: Replicate)</li><li><b>Asat_mean</b>: Mean light-saturated net photosynthesis measured on leaf of a branch that is cut under water and remains in water, calculated from replicated leaves per branch (Field type: Numeric trait)</li><li><b>Asat_sd</b>: Standard deviation of light-saturated net photosynthesis measured on leaf of a branch that is cut under water and remains in water, calculated from replicated leaves per branch (Field type: Numeric)</li><li><b>Asat_n</b>: Number of replicates, i.e. leaves per branch used for mean trait (Field type: Replicate)</li><li><b>Amax_mean</b>: Mean maximum photosynthetic capacity measured on leaf of a branch that is cut under water and remains in water, calculated from replicated leaves per branch (Field type: Numeric trait)</li><li><b>Amax_sd</b>: Standard deviation of maximum photosynthetic capacity measured on leaf of a branch that is cut under water and remains in water, calculated from replicated leaves per branch (Field type: Numeric)</li><li><b>Amax_n</b>: Number of replicates, i.e. leaves per branch used for mean trait (Field type: Replicate)</li><li><b>LA_cm2_mean</b>: Mean leaf area (LA) calculated from fresh leaves collected from branches, scanned immediately. (Field type: Numeric trait)</li><li><b>LA_cm2_sd</b>: Standard deviation of leaf area (Field type: Numeric)</li><li><b>LA_cm2_n</b>: Number of replicates, i.e. leaves per branch used for mean trait (Field type: Replicate)</li><li><b>leaf_thickness_mm_mean</b>: Mean thickness of leaf (Field type: Numeric trait)</li><li><b>fresh_weight_g_mean</b>: Mean leaf fresh weight (Field type: Numeric trait)</li><li><b>dry_weight_g_mean</b>: Mean leaf oven-dried weight (Field type: Numeric trait)</li><li><b>dry_weight_mg_mean</b>: Mean leaf oven-dried weight (Field type: Numeric trait)</li><li><b>LDMC_mg.g_mean</b>: Leaf dry-matter content (LDMC) is the oven-dry mass (mg) of a leaf, divided by its water-saturated fresh mass (g) mg g–1 (Field type: Numeric trait)</li><li><b>leaf_thickness_mm_sd</b>: Standard deviation of leaf thickness (Field type: Numeric)</li><li><b>fresh_weight_g_sd</b>: Standard deviation of fresh leaf weight (Field type: Numeric)</li><li><b>dry_weight_g_sd</b>: Standard deviation of dry leaf weight (Field type: Numeric)</li><li><b>dry_weight_mg_sd</b>: Standard deviation of dry leaf weight (Field type: Numeric)</li><li><b>LDMC_mg.g_sd</b>: Standard deviation of leaf dry matter content (Field type: Numeric)</li><li><b>leaf_thickness_mm_n</b>: Number of replicates, i.e. leaves per branch used for mean trait (Field type: Replicate)</li><li><b>fresh_weight_g_n</b>: Number of replicates, i.e. leaves per branch used for mean trait (Field type: Replicate)</li><li><b>dry_weight_g_n</b>: Number of replicates, i.e. leaves per branch used for mean trait (Field type: Replicate)</li><li><b>dry_weight_mg_n</b>: Number of replicates, i.e. leaves per branch used for mean trait (Field type: Replicate)</li><li><b>LDMC_mg.g_n</b>: Number of replicates, i.e. leaves per branch used for mean trait (Field type: Replicate)</li><li><b>branch_height_m</b>: Height from where branch sample was taken (Field type: Numeric trait)</li><li><b>chla_mg.g</b>: Foliar chlorophyll a content (Field type: Numeric trait)</li><li><b>chlb_mg.g</b>: Foliar chlorophyll b content (Field type: Numeric trait)</li><li><b>carot_mg.g</b>: Foliar carotenoids content (Field type: Numeric trait)</li><li><b>Fp_N_mm_mean</b>: Mean force to punch leaf, dividing the observed force (N) required to puncture the leaf lamina by the circumference of the instrument's rod (Field type: Numeric trait)</li><li><b>Fp_N_mm_sd</b>: Standard deviation for force to punch (Field type: Numeric trait)</li><li><b>Fp_N_mm_n</b>: Number of replicates, i.e. leaves per branch used for mean trait (Field type: Numeric trait)</li><li><b>specific_Fp_mean</b>: Mean specific force to punch (Fp divided by lamina thickness) (Field type: Numeric trait)</li><li><b>specific_Fp_sd</b>: Standard deviation for force to punch (Field type: Numeric trait)</li><li><b>specific_Fp_n</b>: Number of replicates, i.e. leaves per branch used for mean trait (Field type: Numeric trait)</li><li><b>WD_B</b>: Branch wood density from branch segment with bark (Field type: Numeric trait)</li><li><b>WD_NB</b>: Branch wood density from branch segment without bark (bark removed prior measurement) (Field type: Numeric trait)</li><li><b>hemicellulose_perc</b>: Foliar hemicellulose concentration (Field type: Numeric trait)</li><li><b>cellulose_perc</b>: Foliar cellulose concentration (Field type: Numeric trait)</li><li><b>lignin_recalcitrants_perc</b>: Foliar lignin and recalcitrants concentration (Field type: Numeric trait)</li><li><b>Total_tannin_mg.g</b>: Total foliar tannin concentration (Field type: Numeric trait)</li><li><b>Total_phenol_mg.g</b>: Total foliar phenol concentration (Field type: Numeric trait)</li><li><b>SLA_mm2.mg_mean</b>: Specific leaf area (SLA) determined as the one-sided area of a fresh leaf, divided by its oven-dry mass. (Field type: Numeric trait)</li><li><b>total_K_mg.mm2</b>: Foliar potassium content expressed on leaf area basis (Field type: Numeric trait)</li><li><b>total_Ca_mg.mm2</b>: Foliar calcium content expressed on leaf area basis (Field type: Numeric trait)</li><li><b>total_Mg_mg.mm2</b>: Foliar magnesium content expressed on leaf area basis (Field type: Numeric trait)</li><li><b>total_P_mg.mm2</b>: Foliar phosporus content expressed on leaf area basis (Field type: Numeric trait)</li><li><b>chla_mg.mm2</b>: Foliar chlorophyll a content expressed on leaf area basis (Field type: Numeric trait)</li><li><b>chlb_mg.mm2</b>: Foliar chlorophyll b content expressed on leaf area basis (Field type: Numeric trait)</li><li><b>carot_mg.mm2</b>: Foliar carotenoids content expressed on leaf area basis (Field type: Numeric trait)</li><li><b>tannin_mg.mm2</b>: Foliar tannin content expressed on leaf area basis (Field type: Numeric trait)</li><li><b>phenol_mg_mm2</b>: Foliar phenol content expressed on leaf area basis (Field type: Numeric trait)</li><li><b>N_mg.mm2</b>: Foliar nitrogen content expressed on leaf area basis (Field type: Numeric trait)</li><li><b>C_mg.mm2</b>: Foliar carbon content expressed on leaf area basis (Field type: Numeric trait)</li><li><b>hemicellulose_mg.mm2</b>: Foliar hemicellulose content expressed on leaf area basis (Field type: Numeric trait)</li><li><b>cellulose_mg.mm2</b>: Foliar cellulose content expressed on leaf area basis (Field type: Numeric trait)</li><li><b>lignin_recalcitrants_mg.mm2</b>: Foliar lignin and recalcitrants content expressed on leaf area basis (Field type: Numeric trait)</li></ul></li></ol><p><b>CSP_protocol_Chlorophyll_and_Carotenoids.pdf</b></p><p>Description: Methodology of chlorophyll and carotenoids analysis, Carnegie Spectranomics protocol: https://drive.google.com/file/d/0B58dyv8L3FpMdGw0QWtiZElHQzQ/view</p><p><b>CSP_protocol_Phenols_Tannins_Analysis.pdf</b></p><p>Description: Methodology of phenols and tannins analysis, Carnegie Spectranomics protocol: https://drive.google.com/file/d/0B58dyv8L3FpMcTBHblQwRHdyRE0/view</p><p><b>Date range: </b>2014-05-01 to 2018-09-01</p><p><b>Latitudinal extent: </b>4.5000 to 5.0700</p><p><b>Longitudinal extent: </b>116.7500 to 117.8200</p><p><b>Taxonomic coverage: </b><br> All taxon names are validated against the GBIF backbone taxonomy. If a dataset uses a synonym, the accepted usage is shown followed by the dataset usage in brackets. Taxa that cannot be validated, including new species and other unknown taxa, morphospecies, functional groups and taxonomic levels not used in the GBIF backbone are shown in square brackets.</p><div>Plantae<br> - Tracheophyta<br> -  - Liliopsida<br> -  -  - Poales<br> -  -  -  - Poaceae<br> -  -  -  -  - <i>Dinochloa</i><br> -  -  -  -  -  - <i>Dinochloa trichogona</i><br> -  -  -  -  - <i>Imperata</i><br> -  -  -  -  -  - <i>Imperata cylindrica</i><br> -  -  -  -  - <i>Paspalum</i><br> -  -  -  -  -  - <i>Paspalum virgatum</i><br> -  -  - Zingiberales<br> -  -  -  - Marantaceae<br> -  -  -  -  - <i>Phrynium</i><br> -  -  -  -  -  - <i>Phrynium pubinerve</i><br> -  -  -  - Zingiberaceae<br> -  -  -  -  - <i>Etlingera</i><br> -  - Magnoliopsida<br> -  -  - Asterales<br> -  -  -  - Asteraceae<br> -  -  -  -  - <i>Mikania</i><br> -  -  -  -  -  - <i>Mikania micrantha</i><br> -  -  - Celastrales<br> -  -  -  - Celastraceae<br> -  -  -  -  - <i>Lophopetalum</i><br> -  -  -  -  -  - <i>Lophopetalum beccarianum</i><br> -  -  -  -  -  - <i>Lophopetalum glabrum</i><br> -  -  -  -  -  - <i>Lophopetalum javanicum</i><br> -  -  - Cornales<br> -  -  -  - Cornaceae<br> -  -  -  -  - <i>Alangium</i><br> -  -  -  -  -  - <i>Alangium javanicum</i><br> -  -  -  - Nyssaceae<br> -  -  -  -  - <i>Mastixia</i><br> -  -  -  -  -  - <i>Mastixia trichotoma</i><br> -  -  - Ericales<br> -  -  -  - Ebenaceae<br> -  -  -  -  - <i>Diospyros</i><br> -  -  -  -  -  - <i>Diospyros andamanica</i><br> -  -  -  -  -  - <i>Diospyros curranii</i><br> -  -  -  -  -  - <i>Diospyros daemona</i><br> -  -  -  -  -  - <i>Diospyros dictyoneura</i><br> -  -  -  -  -  - <i>Diospyros macrophylla</i><br> -  -  -  -  -  - <i>Diospyros muricata</i><br> -  -  -  -  -  - <i>Diospyros pilosanthera</i><br> -  -  -  -  -  - <i>Diospyros toposia</i><br> -  -  -  -  -  - <i>Diospyros tuberculata</i><br> -  -  -  - Lecythidaceae<br> -  -  -  -  - <i>Barringtonia</i><br> -  -  -  -  -  - <i>Barringtonia lanceolata</i><br> -  -  -  -  -  - <i>Barringtonia macrostachya</i><br> -  -  -  -  -  - <i>Barringtonia sarcostachys</i><br> -  -  -  -  - <i>Planchonia</i><br> -  -  -  -  -  - <i>Planchonia brevistipitata</i><br> -  -  -  - Pentaphylacaceae<br> -  -  -  -  - <i>Adinandra</i><br> -  -  -  -  -  - <i>Adinandra dumosa</i><br> -  -  -  - Primulaceae<br> -  -  -  -  - <i>Ardisia</i><br> -  -  -  -  -  - <i>Ardisia macrophylla</i><br> -  -  -  -  - <i>Maesa</i><br> -  -  -  -  -  - <i>Maesa macrothyrsa</i><br> -  -  -  - Sapotaceae<br> -  -  -  -  - <i>Madhuca</i><br> -  -  -  -  -  - <i>Madhuca dubardii</i><br> -  -  -  -  -  - <i>Madhuca korthalsii</i><br> -  -  -  -  - <i>Palaquium</i><br> -  -  -  -  -  - <i>Palaquium dasyphyllum</i><br> -  -  -  -  -  - <i>Palaquium obovatum</i><br> -  -  -  -  -  - <i>Palaquium sericeum</i><br> -  -  -  -  - <i>Payena</i><br> -  -  -  -  -  - <i>Payena acuminata</i><br> -  -  -  - Symplocaceae<br> -  -  -  -  - <i>Symplocos</i><br> -  -  -  -  -  - <i>Symplocos fasciculata</i><br> -  -  -  - Theaceae<br> -  -  -  -  - <i>Pyrenaria</i><br> -  -  -  -  -  - <i>Pyrenaria tawauensis</i><br> -  -  - Fabales<br> -  -  -  - Fabaceae<br> -  -  -  -  - <i>Archidendron</i><br> -  -  -  -  -  - <i>Archidendron clypearia</i><br> -  -  -  -  - <i>Crudia</i><br> -  -  -  -  -  - <i>Crudia reticulata</i><br> -  -  -  -  -  - <i>Crudia tenuipes</i><br> -  -  -  -  - <i>Cynometra</i><br> -  -  -  -  -  - <i>Cynometra mirabilis</i><br> -  -  -  -  - <i>Dialium</i><br> -  -  -  -  -  - <i>Dialium indum</i><br> -  -  -  -  -  - <i>Dialium kunstleri</i><br> -  -  -  -  - <i>Fordia</i><br> -  -  -  -  -  - <i>Fordia brachybotrys</i><br> -  -  -  -  -  - <i>Fordia splendidissima</i><br> -  -  -  -  - <i>Sindora</i><br> -  -  -  -  - <i>Spatholobus</i><br> -  -  -  -  -  - <i>Spatholobus macropterus</i><br> -  -  -  - Polygalaceae<br> -  -  -  -  - <i>Xanthophyllum</i><br> -  -  -  -  -  - <i>Xanthophyllum flavescens</i><br> -  -  - Fagales<br> -  -  -  - Fagaceae<br> -  -  -  -  - <i>Castanopsis</i><br> -  -  -  -  -  - <i>Castanopsis hypophoenicea</i><br> -  -  -  -  - <i>Lithocarpus</i><br> -  -  -  -  -  - <i>Lithocarpus blumeanus</i><br> -  -  -  -  -  - <i>Lithocarpus conocarpus</i><br> -  -  -  -  -  - <i>Lithocarpus echinifer</i><br> -  -  -  -  -  - <i>Lithocarpus gracilis</i><br> -  -  -  -  -  - <i>Lithocarpus leptogyne</i><br> -  -  -  -  -  - <i>Lithocarpus sundaicus</i><br> -  -  -  -  - <i>Quercus</i><br> -  -  -  -  -  - <i>Quercus argentata</i><br> -  -  -  -  -  - <i>Quercus lowii</i><br> -  -  -  -  -  - <i>Quercus merrillii</i><br> -  -  -  -  - <i>Trigonobalanus</i><br> -  -  -  -  -  - <i>Trigonobalanus verticillata</i><br> -  -  - Gentianales<br> -  -  -  - Apocynaceae<br> -  -  -  -  - <i>Alstonia</i><br> -  -  -  -  -  - <i>Alstonia angustiloba</i><br> -  -  -  - Rubiaceae<br> -  -  -  -  - <i>Ludekia</i><br> -  -  -  -  -  - <i>Ludekia borneensis</i><br> -  -  -  -  - <i>Nauclea</i><br> -  -  -  -  -  - <i>Nauclea officinalis</i><br> -  -  -  -  -  - <i>Nauclea subdita</i><br> -  -  -  -  - <i>Neolamarckia</i><br> -  -  -  -  -  - <i>Neolamarckia cadamba</i><br> -  -  -  -  - <i>Neonauclea</i><br> -  -  -  -  -  - <i>Neonauclea gigantea</i><br> -  -  -  -  - <i>Psydrax</i><br> -  -  -  -  -  - <i>Psydrax dicoccos</i><br> -  -  -  -  - <i>Uncaria</i><br> -  -  -  -  -  - <i>Uncaria cordata</i><br> -  -  -  -  - <i>Urophyllum</i><br> -  -  -  -  -  - <i>Urophyllum polyneurum</i><br> -  -  - Lamiales<br> -  -  -  - Lamiaceae<br> -  -  -  -  - <i>Callicarpa</i><br> -  -  -  -  -  - <i>Callicarpa pentandra</i><br> -  -  -  - Oleaceae<br> -  -  -  -  - <i>Chionanthus</i><br> -  -  -  -  -  - <i>Chionanthus macrocarpus</i><br> -  -  -  -  -  - <i>Chionanthus pluriflorus</i><br> -  -  - Laurales<br> -  -  -  - Lauraceae<br> -  -  -  -  - <i>Actinodaphne</i><br> -  -  -  -  - <i>Beilschmiedia</i><br> -  -  -  -  -  - <i>Beilschmiedia micrantha</i><br> -  -  -  -  - <i>Caryodaphnopsis</i><br> -  -  -  -  -  - <i>Caryodaphnopsis tonkinensis</i><br> -  -  -  -  - <i>Cryptocarya</i><br> -  -  -  -  -  - <i>Cryptocarya nigra</i><br> -  -  -  -  -  - <i>Cryptocarya nitens</i><br> -  -  -  -  - <i>Dehaasia</i><br> -  -  -  -  -  - <i>Dehaasia caesia</i><br> -  -  -  -  -  - <i>Dehaasia incrassata</i><br> -  -  -  -  - <i>Eusideroxylon</i><br> -  -  -  -  -  - <i>Eusideroxylon zwageri</i><br> -  -  -  -  - <i>Lindera</i><br> -  -  -  -  -  - <i>Lindera lucida</i><br> -  -  -  -  - <i>Litsea</i><br> -  -  -  -  -  - <i>Litsea accedens</i><br> -  -  -  -  -  - <i>Litsea angulata</i><br> -  -  -  -  -  - <i>Litsea caulocarpa</i><br> -  -  -  -  -  - <i>Litsea cordata</i><br> -  -  -  -  -  - <i>Litsea garciae</i><br> -  -  -  -  -  - <i>Litsea grandis</i><br> -  -  -  -  -  - <i>Litsea rubiginosa</i><br> -  -  -  -  - <i>Nothaphoebe</i><br> -  -  -  -  -  - <i>Nothaphoebe umbelliflora</i><br> -  -  -  -  - <i>Phoebe</i><br> -  -  -  -  -  - <i>Phoebe grandis</i><br> -  -  - Magnoliales<br> -  -  -  - Annonaceae<br> -  -  -  -  - <i>Cyathocalyx</i><br> -  -  -  -  - <i>Maasia</i><br> -  -  -  -  -  - <i>Maasia sumatrana</i><br> -  -  -  -  - <i>Miliusa</i><br> -  -  -  -  -  - <i>Miliusa macropoda</i><br> -  -  -  -  - <i>Monoon</i><br> -  -  -  -  - <i>Neo-uvaria</i><br> -  -  -  -  -  - <i>Neo-uvaria acuminatissima</i><br> -  -  -  -  - <i>Orophea</i><br> -  -  -  -  -  - <i>Orophea myriantha</i><br> -  -  -  -  - <i>Phaeanthus</i><br> -  -  -  -  -  - <i>Phaeanthus splendens</i><br> -  -  -  -  - <i>Polyalthia</i><br> -  -  -  -  -  - <i>Polyalthia obliqua</i><br> -  -  -  -  - <i>Pseuduvaria</i><br> -  -  -  -  -  - <i>Pseuduvaria borneensis</i><br> -  -  -  -  - <i>Sageraea</i><br> -  -  -  -  -  - <i>Sageraea elliptica</i><br> -  -  -  -  - <i>Stelechocarpus</i><br> -  -  -  -  -  - <i>Stelechocarpus cauliflorus</i><br> -  -  -  -  - <i>Xylopia</i><br> -  -  -  -  -  - <i>Xylopia ferruginea</i><br> -  -  -  -  -  - <i>Xylopia stenopetala</i><br> -  -  -  - Magnoliaceae<br> -  -  -  -  - <i>Magnolia</i><br> -  -  -  -  -  - <i>Magnolia borneensis</i><br> -  -  -  -  -  - <i>Magnolia liliifera</i><br> -  -  -  -  -  - <i>Magnolia tsiampacca</i><br> -  -  -  - Myristicaceae<br> -  -  -  -  - <i>Horsfieldia</i><br> -  -  -  -  -  - <i>Horsfieldia crassifolia</i><br> -  -  -  -  - <i>Knema</i><br> -  -  -  -  -  - <i>Knema glauca</i><br> -  -  -  -  -  - <i>Knema latifolia</i><br> -  -  -  -  -  - <i>Knema laurina</i><br> -  -  -  -  -  - <i>Knema oblongata</i><br> -  -  -  -  - <i>Myristica</i><br> -  -  -  -  -  - <i>Myristica smythiesii</i><br> -  -  - Malpighiales<br> -  -  -  - Achariaceae<br> -  -  -  -  - <i>Hydnocarpus</i><br> -  -  -  -  -  - <i>Hydnocarpus woodii</i><br> -  -  -  -  - <i>Ryparosa</i><br> -  -  -  -  -  - <i>Ryparosa acuminata</i><br> -  -  -  - Calophyllaceae<br> -  -  -  -  - <i>Calophyllum</i><br> -  -  -  -  -  - <i>Calophyllum soulattri</i><br> -  -  -  -  -  - <i>Calophyllum woodii</i><br> -  -  -  -  - <i>Mesua</i><br> -  -  -  -  -  - <i>Mesua borneensis</i><br> -  -  -  -  -  - <i>Mesua macrantha</i><br> -  -  -  -  -  - <i>Mesua oblongifolia</i><br> -  -  -  - Centroplacaceae<br> -  -  -  -  - <i>Bhesa</i><br> -  -  -  -  -  - <i>Bhesa indica</i><br> -  -  -  - Chrysobalanaceae<br> -  -  -  -  - <i>Atuna</i><br> -  -  -  -  -  - <i>Atuna racemosa</i><br> -  -  -  -  - <i>Licania</i><br> -  -  -  -  -  - <i>Licania splendens</i><br> -  -  -  - Clusiaceae<br> -  -  -  -  - <i>Garcinia</i><br> -  -  -  -  -  - <i>Garcinia benthamiana</i><br> -  -  -  -  -  - <i>Garcinia forbesii</i><br> -  -  -  -  -  - <i>Garcinia nervosa</i><br> -  -  -  -  -  - <i>Garcinia parvifolia</i><br> -  -  -  - Euphorbiaceae<br> -  -  -  -  - <i>Blumeodendron</i><br> -  -  -  -  -  - <i>Blumeodendron kurzii</i><br> -  -  -  -  -  - <i>Blumeodendron tokbrai</i><br> -  -  -  -  - <i>Hancea</i><br> -  -  -  -  -  - <i>Hancea penangensis</i><br> -  -  -  -  - <i>Macaranga</i><br> -  -  -  -  -  - <i>Macaranga conifera</i><br> -  -  -  -  -  - <i>Macaranga gigantea</i><br> -  -  -  -  -  - <i>Macaranga hypoleuca</i><br> -  -  -  -  -  - <i>Macaranga pearsonii</i><br> -  -  -  -  -  - <i>Macaranga winkleri</i><br> -  -  -  -  - <i>Mallotus</i><br> -  -  -  -  -  - <i>Mallotus leucodermis</i><br> -  -  -  -  -  - <i>Mallotus miquelianus</i><br> -  -  -  -  -  - <i>Mallotus mollissimus</i><br> -  -  -  -  -  - <i>Mallotus wrayi</i><br> -  -  -  -  - <i>Neoscortechinia</i><br> -  -  -  -  -  - <i>Neoscortechinia kingii</i><br> -  -  -  -  -  - <i>Neoscortechinia philippinensis</i><br> -  -  -  -  - <i>Ptychopyxis</i><br> -  -  -  -  -  - <i>Ptychopyxis arborea</i><br> -  -  -  -  - <i>Spathiostemon</i><br> -  -  -  - Hypericaceae<br> -  -  -  -  - <i>Cratoxylum</i><br> -  -  -  - Irvingiaceae<br> -  -  -  -  - <i>Irvingia</i><br> -  -  -  -  -  - <i>Irvingia malayana</i><br> -  -  -  - Phyllanthaceae<br> -  -  -  -  - <i>Antidesma</i><br> -  -  -  -  - <i>Aporosa</i><br> -  -  -  -  -  - <i>Aporosa confusa</i><br> -  -  -  -  -  - <i>Aporosa falcifera</i><br> -  -  -  -  - <i>Baccaurea</i><br> -  -  -  -  -  - <i>Baccaurea lanceolata</i><br> -  -  -  -  -  - <i>Baccaurea macrocarpa</i><br> -  -  -  -  -  - <i>Baccaurea pubera</i><br> -  -  -  -  -  - <i>Baccaurea tetrandra</i><br> -  -  -  -  - <i>Cleistanthus</i><br> -  -  -  -  -  - <i>Cleistanthus hirsutulus</i><br> -  -  -  -  -  - <i>Cleistanthus hylandii</i><br> -  -  -  -  -  - <i>Cleistanthus oblongifolius</i><br> -  -  -  -  -  - <i>Cleistanthus paxii</i><br> -  -  -  -  -  - <i>Cleistanthus pubens</i><br> -  -  -  -  - <i>Glochidion</i><br> -  -  -  -  -  - <i>Glochidion borneensis</i><br> -  -  -  -  - <i>Phyllanthus</i><br> -  -  -  -  -  - <i>Phyllanthus lutescens</i><br> -  -  -  -  -  - <i>Phyllanthus ruber</i><br> -  -  -  - Putranjivaceae<br> -  -  -  -  - <i>Drypetes</i><br> -  -  -  -  -  - <i>Drypetes longifolia</i><br> -  -  -  - Salicaceae<br> -  -  -  -  - <i>Flacourtia</i><br> -  -  -  -  -  - <i>Flacourtia rukam</i><br> -  -  -  -  - <i>Homalium</i><br> -  -  -  -  -  - <i>Homalium foetidum</i><br> -  -  - Malvales<br> -  -  -  - Dipterocarpaceae<br> -  -  -  -  - <i>Dipterocarpus</i><br> -  -  -  -  -  - <i>Dipterocarpus caudiferus</i><br> -  -  -  -  - <i>Dryobalanops</i><br> -  -  -  -  -  - <i>Dryobalanops lanceolata</i><br> -  -  -  -  - <i>Hopea</i><br> -  -  -  -  -  - <i>Hopea plagata</i><br> -  -  -  -  -  - <i>Hopea sangal</i><br> -  -  -  -  - <i>Parashorea</i><br> -  -  -  -  -  - <i>Parashorea malaanonan</i><br> -  -  -  -  -  - <i>Parashorea smythiesii</i><br> -  -  -  -  -  - <i>Parashorea warburgii</i><br> -  -  -  -  - <i>Shorea</i><br> -  -  -  -  -  - <i>Shorea almon</i><br> -  -  -  -  -  - <i>Shorea angustifolia</i><br> -  -  -  -  -  - <i>Shorea argentifolia</i><br> -  -  -  -  -  - <i>Shorea beccariana</i><br> -  -  -  -  -  - <i>Shorea faguetiana</i><br> -  -  -  -  -  - <i>Shorea falciferoides</i><br> -  -  -  -  -  - <i>Shorea fallax</i><br> -  -  -  -  -  - <i>Shorea gibbosa</i><br> -  -  -  -  -  - <i>Shorea guiso</i><br> -  -  -  -  -  - <i>Shorea johorensis</i><br> -  -  -  -  -  - <i>Shorea laevis</i><br> -  -  -  -  -  - <i>Shorea leprosula</i><br> -  -  -  -  -  - <i>Shorea leptoderma</i><br> -  -  -  -  -  - <i>Shorea macrophylla</i><br> -  -  -  -  -  - <i>Shorea macroptera</i><br> -  -  -  -  -  - <i>Shorea ovalis</i><br> -  -  -  -  -  - <i>Shorea ovata</i><br> -  -  -  -  -  - <i>Shorea parvifolia</i><br> -  -  -  -  -  - <i>Shorea parvistipulata</i><br> -  -  -  -  -  - <i>Shorea pauciflora</i><br> -  -  -  -  -  - <i>Shorea pinanga</i><br> -  -  -  -  -  - <i>Shorea superba</i><br> -  -  -  -  -  - <i>Shorea symingtonii</i><br> -  -  -  -  -  - <i>Shorea xanthophylla</i><br> -  -  -  -  - <i>Vatica</i><br> -  -  -  -  -  - <i>Vatica dulitensis</i><br> -  -  -  -  -  - <i>Vatica odorata</i><br> -  -  -  - Malvaceae<br> -  -  -  -  - <i>Boschia</i><br> -  -  -  -  -  - <i>Boschia grandiflora</i><br> -  -  -  -  - <i>Durio</i><br> -  -  -  -  -  - <i>Durio graveolens</i><br> -  -  -  -  - <i>Heritiera</i><br> -  -  -  -  -  - <i>Heritiera elata</i><br> -  -  -  -  - <i>Microcos</i><br> -  -  -  -  -  - <i>Microcos crassifolia</i><br> -  -  -  -  - <i>Pentace</i><br> -  -  -  -  -  - <i>Pentace borneensis</i><br> -  -  -  -  - <i>Pterygota</i><br> -  -  -  -  -  - <i>Pterygota alata</i><br> -  -  -  -  - <i>Scaphium</i><br> -  -  -  -  -  - <i>Scaphium macropodum</i><br> -  -  -  -  - <i>Sterculia</i><br> -  -  -  -  -  - <i>Sterculia rubiginosa</i><br> -  -  -  -  -  - <i>Sterculia stipulata</i><br> -  -  -  - Thymelaeaceae<br> -  -  -  -  - <i>Aquilaria</i><br> -  -  -  -  -  - <i>Aquilaria beccariana</i><br> -  -  - Myrtales<br> -  -  -  - Combretaceae<br> -  -  -  -  - <i>Terminalia</i><br> -  -  -  -  -  - <i>Terminalia citrina</i><br> -  -  -  -  -  - <i>Terminalia foetidissima</i><br> -  -  -  - Lythraceae<br> -  -  -  -  - <i>Duabanga</i><br> -  -  -  -  -  - <i>Duabanga moluccana</i><br> -  -  -  - Melastomataceae<br> -  -  -  -  - <i>Clidemia</i><br> -  -  -  -  -  - <i>Clidemia hirta</i><br> -  -  -  -  - <i>Melastoma</i><br> -  -  -  -  -  - <i>Melastoma malabathricum</i><br> -  -  -  -  - <i>Memecylon</i><br> -  -  -  -  -  - <i>Memecylon oleifolium</i><br> -  -  -  - Myrtaceae<br> -  -  -  -  - <i>Syzygium</i><br> -  -  -  -  -  - <i>Syzygium caudatilimbum</i><br> -  -  -  -  -  - <i>Syzygium chloranthum</i><br> -  -  -  -  -  - <i>Syzygium elopurae</i><br> -  -  -  -  -  - <i>Syzygium grande</i><br> -  -  -  -  -  - <i>Syzygium griffithii</i><br> -  -  -  -  -  - <i>Syzygium kunstleri</i><br> -  -  -  -  -  - <i>Syzygium lineatum</i><br> -  -  -  -  -  - <i>Syzygium pancheri</i><br> -  -  -  -  -  - <i>Syzygium panzeri</i><br> -  -  -  -  -  - <i>Syzygium pustulatum</i><br> -  -  -  -  -  - <i>Syzygium racemosum</i><br> -  -  -  -  -  - <i>Syzygium rheophyticum</i><br> -  -  -  -  - <i>Tristaniopsis</i><br> -  -  -  -  -  - <i>Tristaniopsis whiteana</i><br> -  -  - Oxalidales<br> -  -  -  - Elaeocarpaceae<br> -  -  -  -  - <i>Elaeocarpus</i><br> -  -  -  -  -  - <i>Elaeocarpus floribundus</i><br> -  -  -  -  -  - <i>Elaeocarpus pedunculatus</i><br> -  -  -  -  -  - <i>Elaeocarpus stipularis</i><br> -  -  -  -  - <i>Sloanea</i><br> -  -  -  -  -  - <i>Sloanea javanica</i><br> -  -  - Rosales<br> -  -  -  - Cannabaceae<br> -  -  -  -  - <i>Gironniera</i><br> -  -  -  -  -  - <i>Gironniera nervosa</i><br> -  -  -  -  - <i>Trema</i><br> -  -  -  -  -  - <i>Trema orientalis</i><br> -  -  -  - Moraceae<br> -  -  -  -  - <i>Antiaris</i><br> -  -  -  -  -  - <i>Antiaris toxicaria</i><br> -  -  -  -  - <i>Artocarpus</i><br> -  -  -  -  -  - <i>Artocarpus anisophyllus</i><br> -  -  -  -  -  - <i>Artocarpus glaucus</i><br> -  -  -  -  -  - <i>Artocarpus integer</i><br> -  -  -  -  -  - <i>Artocarpus odoratissimus</i><br> -  -  -  -  -  - <i>Artocarpus tamaran</i><br> -  -  -  -  - <i>Ficus</i><br> -  -  -  -  -  - <i>Ficus hispida</i><br> -  -  -  -  -  - <i>Ficus septica</i><br> -  -  -  -  -  - <i>Ficus uncinata</i><br> -  -  -  -  -  - <i>Ficus variegata</i><br> -  -  -  - Rosaceae<br> -  -  -  -  - <i>Prunus</i><br> -  -  -  -  -  - <i>Prunus javanica</i><br> -  -  -  -  - <i>Pygeum</i><br> -  -  -  -  -  - <i>Pygeum beccarii</i><br> -  -  -  - Urticaceae<br> -  -  -  -  - <i>Dendrocnide</i><br> -  -  -  -  -  - <i>Dendrocnide elliptica</i><br> -  -  - Santalales<br> -  -  -  - Coulaceae<br> -  -  -  -  - <i>Ochanostachys</i><br> -  -  -  -  -  - <i>Ochanostachys amentacea</i><br> -  -  -  - Strombosiaceae<br> -  -  -  -  - <i>Scorodocarpus</i><br> -  -  -  -  -  - <i>Scorodocarpus borneensis</i><br> -  -  - Sapindales<br> -  -  -  - Anacardiaceae<br> -  -  -  -  - <i>Gluta</i><br> -  -  -  -  -  - <i>Gluta aptera</i><br> -  -  -  -  -  - <i>Gluta wallichii</i><br> -  -  -  -  - <i>Mangifera</i><br> -  -  -  -  -  - <i>Mangifera odorata</i><br> -  -  -  -  - <i>Melanochyla</i><br> -  -  -  -  -  - <i>Melanochyla bullata</i><br> -  -  -  -  -  - <i>Melanochyla tomentosa</i><br> -  -  -  -  - <i>Parishia</i><br> -  -  -  -  -  - <i>Parishia insignis</i><br> -  -  -  - Burseraceae<br> -  -  -  -  - <i>Canarium</i><br> -  -  -  -  -  - <i>Canarium decumanum</i><br> -  -  -  -  -  - <i>Canarium denticulatum</i><br> -  -  -  -  -  - <i>Canarium odontophyllum</i><br> -  -  -  -  -  - <i>Canarium pilosum</i><br> -  -  -  -  - <i>Dacryodes</i><br> -  -  -  -  -  - <i>Dacryodes rostrata</i><br> -  -  -  -  -  - <i>Dacryodes rugosa</i><br> -  -  -  -  - <i>Santiria</i><br> -  -  -  -  -  - <i>Santiria laevigata</i><br> -  -  -  - Meliaceae<br> -  -  -  -  - <i>Aglaia</i><br> -  -  -  -  -  - <i>Aglaia crassinervia</i><br> -  -  -  -  -  - <i>Aglaia leptantha</i><br> -  -  -  -  -  - <i>Aglaia macrocarpa</i><br> -  -  -  -  -  - <i>Aglaia odoratissima</i><br> -  -  -  -  -  - <i>Aglaia oligophylla</i><br> -  -  -  -  -  - <i>Aglaia silvestris</i><br> -  -  -  -  -  - <i>Aglaia tomentosa</i><br> -  -  -  -  - <i>Aphanamixis</i><br> -  -  -  -  -  - <i>Aphanamixis polystachya</i><br> -  -  -  -  - <i>Chisocheton</i><br> -  -  -  -  -  - <i>Chisocheton ceramicus</i><br> -  -  -  -  -  - <i>Chisocheton macranthus</i><br> -  -  -  -  -  - <i>Chisocheton patens</i><br> -  -  -  -  - <i>Dysoxylum</i><br> -  -  -  -  -  - <i>Dysoxylum cyrtobotryum</i><br> -  -  -  -  -  - <i>Dysoxylum densiflorum</i><br> -  -  -  -  - <i>Lansium</i><br> -  -  -  -  -  - <i>Lansium domesticum</i><br> -  -  -  -  - <i>Reinwardtiodendron</i><br> -  -  -  -  -  - <i>Reinwardtiodendron humile</i><br> -  -  -  -  - <i>Walsura</i><br> -  -  -  -  -  - <i>Walsura pinnata</i><br> -  -  -  - Rutaceae<br> -  -  -  -  - <i>Melicope</i><br> -  -  -  -  -  - <i>Melicope confusa</i><br> -  -  -  - Sapindaceae<br> -  -  -  -  - <i>Dimocarpus</i><br> -  -  -  -  -  - <i>Dimocarpus longan</i><br> -  -  -  -  - <i>Nephelium</i><br> -  -  -  -  -  - <i>Nephelium cuspidatum</i><br> -  -  -  -  - <i>Paranephelium</i><br> -  -  -  -  -  - <i>Paranephelium macrophyllum</i><br> -  -  -  -  -  - <i>Paranephelium xestophyllum</i><br> -  -  -  -  - <i>Pometia</i><br> -  -  -  -  -  - <i>Pometia pinnata</i><br> -  -  -  -  - <i>Tristiropsis</i><br> -  -  -  -  -  - <i>Tristiropsis acutangula</i><br> -  -  - Solanales<br> -  -  -  - Convolvulaceae<br> -  -  -  -  - <i>Decalobanthus</i><br> -  -  -  -  -  - <i>Decalobanthus borneensis</i><br> -  -  -  -  - <i>Jacquemontia</i><br> -  -  -  -  -  - <i>Jacquemontia tomentella</i><br> -  - Polypodiopsida<br> -  -  - Gleicheniales<br> -  -  -  - Gleicheniaceae<br> -  -  -  -  - <i>Dicranopteris</i><br> -  -  -  -  -  - <i>Dicranopteris pubigera</i><br> -  -  - Polypodiales<br> -  -  -  - Lomariopsidaceae<br> -  -  -  -  - <i>Nephrolepis</i><br> -  -  -  -  -  - <i>Nephrolepis biserrata</i><br></div><p></p>
Figure 3 in First record of the saproxylic beetle Corticeus (= Hypophloeus) unicolor Piller & Mitterpacher, 1783 in Montenegro (Coleoptera: Tenebrionidae) with comments on old-growth forests conservation in the Country
Figure 3. Mixed beech–silver fir–Norway spruce old-growth forest, snag and coarse woody debrys in Biogradska gora National Park, where Corticeus unicolor was collected.
Figure 2 in First record of the saproxylic beetle Corticeus (= Hypophloeus) unicolor Piller & Mitterpacher, 1783 in Montenegro (Coleoptera: Tenebrionidae) with comments on old-growth forests conservation in the Country
Figure 2. Corticeus unicolor: (A) side view and (B) view from above (B). Scale bar: 1 mm. Photos by F. Parisi.
Data from: Vegetation dynamics 1946–2018 in an old-growth conifer forest
Open the record for dataset details and reuse information.
Data from: The effect of drainage on the fine root biomass, production, and turnover in hemiboreal old-growth forests on organic soils
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X-ray imaging of 30 year old wine grape wood reveals cumulative impacts of rootstocks on scion secondary growth and harvest index
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Raw count data from repeated surveys of a guild of Plethodon salamanders in an old-growth forest in southeastern Kentucky 2016, with GIS and in situ environmental data
Woodland salamanders are among the most abundant vertebrate animals in temperate deciduous forests of eastern North America. Because of their abundance, woodland salamanders are responsible for the transformation of nutrients and translocation of energy between highly disparate levels of trophic organization: detrital food webs and high-order predators. However, the spatial extent of woodland salamanders’ role in the ecosystem is likely contingent upon the distribution of their biomass throughout the forest. We sought to determine if natural environmental gradients influence the fine-scale distribution and density of Southern Ravine Salamanders (Plethodon richmondi) and Cumberland Plateau Salamanders (P. kentucki). We addressed this objective by constructing occupancy, co-occurrence, and abundance models from temporally-replicated surveys within an old-growth forest in the Cumberland Plateau region of Kentucky occurring in the Fall of 2016. We found that Plethodon richmondi had a more restricted fine-scale distribution than P. kentucki (mean occupancy probability = 0.737) and exhibited variable density, from less than 250 to greater than 1000 individuals per hectare, associated with increased soil moisture and reduced solar exposure due to slope face. While more ubiquitously distributed (mean occupancy probability = 0.95), P. kentucki density varied from less than 400 to greater than 1000 individuals per hectare and was inversely related to increased solar exposure from canopy disturbance and landscape convexity. Our data suggest co-occurrence patterns of P. richmondi and P. kentucki are influenced primarily by abiotic conditions within the forest, and that populations likely occur independently and without evidence of biotic interaction. Given the critical role that woodland salamanders play in the maintenance of forest health, regions that support large populations of woodland salamanders, such as those highlighted in this study—mesic forest stands on north-to-eas
Soil Moisture and vegetation cover patterns after logging and burning an old-growth Douglas-fir forest in the Andrews Experimental Forest, 1960-1983
This soil moisture study was initiated in 1960 to investigate the effects of patch clearcut logging and slash burning (1962-63) in an old-growth Douglas-fir forest in the Oregon Cascade Range. Since soil moisture and vegetation sampling continued regularly until 1980, this is a unique data set that represents nearly two decades of post-treatment information. Plant cover exerts a profound influence on soil moisture levels through its effects on interception, infiltration, evaporation, and transpiration. In the Douglas-fir forests of the Pacific Northwest, clearcut logging and slash burning are common practices that can dramatically alter plant cover and soil moisture. Logging can increase soil moisture by temporarily reducing cover and associated water use, and burning may further augment soil moisture levels by suppressing the survival and regrowth of vegetation. Indeed, part of the rationale for slash burning in the region is to control shrubs and other vegetation that would otherwise compete with conifer seedlings for available moisture, light, and nutrients. Within a few years after burning, however, invading vegetation may deplete soil moisture to levels comparable to forested areas. Such observations point to the value of long-term information to better understand dynamic soil moisture and plant cover responses to forest practices.
Over 80 years without major disturbance, late successional Białowieża woodlands exhibit complex dynamism, with coherent compositional shifts towards true old‐growth conditions
<p>1. Controversies about successional dynamics of woodland communities have a long history, dating back to the classical debates between Clements and Gleason and continuing into the present. These debates have largely concerned the predictability or convergence of forest developmental trends as well as the relative importance of different mechanisms and forces driving forest succession. However, opportunities for rigorous testing of competing hypotheses are limited, mainly because plot-based studies of forest vegetation spanning more than a decade are scarce and even fewer concern late-successional stands.</p> <p>2. We exploit a unique long-term data set from mesic temperate forests of eastern Poland, spanning ca. 80 years (1936-2012) in strictly protected, late-successional woodlands assigned to seven different 'structural types'. We use non-metric multidimensional scaling to assess stability of species composition over the study period. We examine predictability of composition and change trajectories over time using Mantel statistics, and we examine changes in distributions of dissimilarity indices to assess convergence or divergence at the examined time and spatial scales.</p> <p>3. Tree communities in Białowieża Forest have changed substantially over the last eight decades. Several species (aspen, birch, pine, oak, ash, maple and spruce) exhibited large decreases in density, while few other species (especially hornbeam and lime) have increased in importance across a wide range of initial compositional types. Forest types recognized in earlier periods have become much less distinguishable. Metrics do not yet show clear successional convergence, mainly due to a) declines in the previously broadly distributed spruce and b) persistence of large individuals of intermediate, long-lived species (even though these species lack significant regeneration).</p> <p>4. Synthesis. Late-successional woodland communities of Białowieża Forest are clearly dynamic and do not show quasi-equilibrial properties often assumed of old-growth forests. Forest types previously recognized as distinct have become progressively less differentiated. Plausible explanations invoke alteration in competitive relationships due to complex changes in environment, including climate, N deposition, natural and human disturbance, and ungulate herbivory over 70 years. Hornbeam and lime have been favored over spruce, pine, oak and birch, although the resulting successional convergence is far from complete at this time. In the absence of major disturbance, we expect future decades to show continued and successional homogenization.</p>
Data from: microhabitat selection by the Oscura Mountains Colorado chipmunk (Neotamias quadrivittatus oscuraensis): an old growth pinyon-juniper woodland specialist
<p>Habitat specialists have been largely overlooked in old growth pinyon-juniper woodlands, despite specialists exhibiting heightened sensitivity to anthropogenic habitat loss. Furthermore, small mammal relationships within pinyon-juniper woodlands have most commonly been investigated via species abundance or habitat use, rather than habitat selection, thereby providing limited management metrics. We used the Oscura Mountains Colorado chipmunk (<em>Neotamias quadrivittatus oscuraensis</em>) as a model organism to evaluate whether old growth conditions drive resource selection by small mammals associated with pinyon-juniper woodlands. The goal of our study was to determine resources important to the chipmunk to inform management decisions. We evaluated microhabitat selection by testing a priori predictions based on natural history characteristics of the chipmunk and the woodlands. We grouped predictions into habitat characteristics affiliated with or not affiliated with old growth. We tested predictions under a multi-stage modeling framework using generalized linear mixed models with a binomial response variable of use versus availability. Probability of selection by chipmunks increased with increasing mean juniper diameter and increasing variation of pinyon diameter and decreased with increased distance to rocky escape terrain and increased mean percent grass cover. Our findings support the classification of the Oscura Mountains Colorado chipmunk as an old growth pinyon-juniper specialist, as the chipmunk displayed disproportionate preference for old growth microhabitat conditions. We recommend management policies that conserve old growth multi-age stands of pinyons and junipers. Old growth conditions near outcroppings, escarpments, and large boulders are of particular conservation concern. Further, thinning resulting in increased grass cover may be detrimental to this old growth pinyon-juniper specialist.</p>
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Allen Brain Atlas
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Annotated Behaviour and Observability Dataset (ABODe)
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