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Fig. 2 in Dispersal of the zoophytophagous predator Brontocoris tabidus and Podisus nigrispinus (Heteroptera: Pentatomidae) in an eucalyptus plantation
Fig. 2. Daily dispersal distance of the predators Brontocoris tabidus and Podisus nigrispinus (Heteroptera: Pentatomidae) in a clonal eucalyptus Eucalyptus grandis × Eucalyptus urophylla plantation in ViÇosa, Minas Gerais State, Brazil. Means followed by the same letter, uppercase or lowercase, do not differ according to the Scott-Knott test with P <0.05.
Fig. 4 in Dispersal of the zoophytophagous predator Brontocoris tabidus and Podisus nigrispinus (Heteroptera: Pentatomidae) in an eucalyptus plantation
Fig. 4. Distance traveled by the predators Brontocoris tabidus (A) and Podisus nigrispinus (B) (Heteroptera: Pentatomidae) males and females in a clonal eucalyptus plantation (Eucalyptus grandis × Eucalyptus urophylla) 7 d afer release. Means followed by the same letter do not differ according to the F test with P <0.05.
Fig. 1. Experimental design showing the 6 in Dispersal of the zoophytophagous predator Brontocoris tabidus and Podisus nigrispinus (Heteroptera: Pentatomidae) in an eucalyptus plantation
Fig. 1. Experimental design showing the 6 sample areas in the ViÇosa Municipality, Minas Gerais State, Brazil. Map was produced with QGIS version 2.18.3 (Open Source Geospatial Foundation Project, http://www.qgis.org/ [last accessed 16 Dec 2019]).
Fig. 3 in Dispersal of the zoophytophagous predator Brontocoris tabidus and Podisus nigrispinus (Heteroptera: Pentatomidae) in an eucalyptus plantation
Fig. 3. Distance traveled by the predators Brontocoris tabidus (A) and Podisus nigrispinus (B) (Heteroptera: Pentatomidae) up to 60 m from release point in a clonal eucalyptus plantation (Eucalyptus grandis × Eucalyptus urophylla) during a 7 d evaluation.
Datasets for manuscipt Use of Weighted Voronoi diagram for forest thinning proposal and skidding trail layout for teak plantation in Thailand
<p>Project package used in manuscript entitled: Use of Weighted Voronoi diagram for forest thinning proposal and skidding trail layout for teak plantation in Thailand. Project package can be open in ArcGIS Pro and contains raster datasets and shapefiles. Zip file contains unpacked package into the folder with spatial data and project file (APRX). </p>
A dataset of estimated net primary production of Japanese cedar plantations (ver.1)
<p># Abbreviations in this text<br> NPP: Net Primary Production, average of stand ages 36-40<br> GCM: Global Climate Model<br> HT: Historical Trend, average of five years 1996-2000<br> FP2050: Future Prediction, average of five years 2046-2050<br> FP2100: Future Prediction, average of five years 2096-2100 (except for a GCM HadGEM2-ES of 2095-2099)</p> <p># Description<br> The data is prepared as four files in tab-delimited text format or ten netcdf files in a zip file. The annual NPP of cedar plantations under current and future climates are calculated in 196928 meshes in Japan. The climate scenarios used are owned and distributed by the third party (National Agriculture and Food Research Organization, Japan). For the methodology on modeling, parameterization and nation-wide calculation, please check the paper below.</p> <p># Reference<br> Toriyama J, Hashimoto S, Osone Y, Yamashita N, Tsurita T, Shimizu T, Saitoh TM, Sawano S, Lehtonen A, Ishizuka S (2021) Estimating spatial variation in the effects of climate change on the net primary production of Japanese cedar plantations based on modeled carbon dynamics. PLoS ONE 16(2): e0247165. https://doi.org/10.1371/journal.pone.0247165</p> <p># List of variables in text files</p> <p># site.txt (6.8 MB)<br> mesh: Number of third-mesh order in the Japanese grid square system<br> lat: Latitude (degree) of center point of third-mesh order<br> long: Longitude (degree) of center point of third-mesh order<br> block: Block number in Toriyama et al. (2021), 1, 2 and 3 for SW, CT and NW, respectively<br> pref: Prefecture number in the Japanese administrative system</p> <p># npp_2000.txt (8.7 MB)<br> mesh: Number of third-mesh order in the Japanese grid square system<br> npp_2000_cgcm: Annual NPP (kgC m-2 year-1) in HT, MRI-CGCM3<br> npp_2000_csiro: Annual NPP (kgC m-2 year-1) in HT, CSIRO-Mk3-6-0<br> npp_2000_gfdl: Annual NPP (kgC m-2 year-1) in HT, GFDL-CM3<br> npp_2000_hadgem: Annual NPP (kgC m-2 year-1) in HT, HadGEM2-ES<br> npp_2000_miroc: Annual NPP (kgC m-2 year-1) in HT, MIROC5</p> <p># npp_2050.txt (15.4 MB)<br> mesh: Number of third-mesh order in the Japanese grid square system<br> npp_rcp26_2050_cgcm: Annual NPP (kgC m-2 year-1) in FP2050, RCP2.6, MRI-CGCM3<br> npp_rcp26_2050_csiro: Annual NPP (kgC m-2 year-1) in FP2050, RCP2.6, CSIRO-Mk3-6-0<br> npp_rcp26_2050_gfdl: Annual NPP (kgC m-2 year-1) in FP2050, RCP2.6, GFDL-CM3<br> npp_rcp26_2050_hadgem: Annual NPP (kgC m-2 year-1) in FP2050, RCP2.6, HadGEM2-ES<br> npp_rcp26_2050_miroc: Annual NPP (kgC m-2 year-1) in FP2050, RCP2.6, MIROC5<br> npp_rcp85_2050_cgcm: Annual NPP (kgC m-2 year-1) in FP2050, RCP8.5, MRI-CGCM3<br> npp_rcp85_2050_csiro: Annual NPP (kgC m-2 year-1) in FP2050, RCP8.5, CSIRO-Mk3-6-0<br> npp_rcp85_2050_gfdl: Annual NPP (kgC m-2 year-1) in FP2050, RCP8.5, GFDL-CM3<br> npp_rcp85_2050_hadgem: Annual NPP (kgC m-2 year-1) in FP2050, RCP8.5, HadGEM2-ES<br> npp_rcp85_2050_miroc: Annual NPP (kgC m-2 year-1) in FP2050, RCP8.5, MIROC5</p> <p># npp_2100.txt (15.4 MB)<br> mesh: Number of third-mesh order in the Japanese grid square system<br> npp_rcp26_2100_cgcm: Annual NPP (kgC m-2 year-1) in FP2100, RCP2.6, MRI-CGCM3<br> npp_rcp26_2100_csiro: Annual NPP (kgC m-2 year-1) in FP2100, RCP2.6, CSIRO-Mk3-6-0<br> npp_rcp26_2100_gfdl: Annual NPP (kgC m-2 year-1) in FP2100, RCP2.6, GFDL-CM3<br> npp_rcp26_2100_hadgem: Annual NPP (kgC m-2 year-1) in FP2100, RCP2.6, HadGEM2-ES<br> npp_rcp26_2100_miroc: Annual NPP (kgC m-2 year-1) in FP2100, RCP2.6, MIROC5<br> npp_rcp85_2100_cgcm: Annual NPP (kgC m-2 year-1) in FP2100, RCP8.5, MRI-CGCM3<br> npp_rcp85_2100_csiro: Annual NPP (kgC m-2 year-1) in FP2100, RCP8.5, CSIRO-Mk3-6-0<br> npp_rcp85_2100_gfdl: Annual NPP (kgC m-2 year-1) in FP2100, RCP8.5, GFDL-CM3<br> npp_rcp85_2100_hadgem: Annual NPP (kgC m-2 year-1) in FP2100, RCP8.5, HadGEM2-ES<br> npp_rcp85_2100_miroc: Annual NPP (kgC m-2 year-1) in FP2100, RCP8.5, MIROC5</p> <p># npp_netcdf.zip (594 MB)<br> The 10 files in netcdf format are compiled in a zip file for NPP data of different RCP scenarios and GCMs.<br> Please check the content of each file by following command.<br> ncdump -h filename</p> <p># summary_map.zip (5.8 MB)<br> The 20 files in png format are compiled in a zip file for maps of NPP and its change. The maps were created using the Generic Mapping Tools version 5 (http://gmt.soest.hawaii.edu/). The average values of five GCMs are used for mapping.</p> <p># Acknowledgement<br> This dataset was funded by the Agriculture, Forestry and Fisheries Research Council in Japan, under the project “Research on adaptation to climate change for agriculture, forestry and fisheries”.</p>
Data from: Native shade trees aid bird conservation in tea plantations in southern India
<p>In the Western Ghats, India, we study how different intensities of tea cultivation influence birds. We compared bird communities in conventional monoculture tea and mixed-shade tea plantations, both of which use agrochemicals, with organic tea plantations, a rainforest fragment, and continuous rainforest within the Anamalai Tiger Reserve. In 225 point count surveys, overall bird species richness and abundance were lowest in conventional tea and up to 33% higher in organic tea. Mixed-shade tea had 40% higher species richness (including 15 canopy and 4 shrub and mid-storey species – primarily frugivores, nectarivores and insectivores), and 83% higher bird abundance than conventional tea, with a greater proportion of forest-affiliated birds and similarity in species composition with forest sites. The rainforest fragment and continuous rainforest had a higher proportion, richness and abundance of forest-affiliated birds and fewer open-country birds, unlike tea plantations where the pattern was reversed. Habitat associations of 62 bird species in indicator species analysis revealed similar patterns. Thus organic tea is better than conventional tea for birds, but mixed-shade tea is even better, although still poorer than forests. Retaining or promoting native shade trees in tea plantations will increase bird diversity and abundance, including of forest-affiliated species and support landscape-level bird conservation.</p>
Figure 2 in Edaphic characteristics and environmental impact of rubber tree plantations on soil mite (Acari) communities
Figure 2 Abundance logarithmic transformation – logx (+1) of Gamasida (A) and Oribatida (B) major groups across the land use types. SF: secondary forests, R7: 7-year-old rubber plantations, R12: 12- year-old rubber plantations, R25: 25-year-old rubber plantations. N = 120; one-way ANOVA test,p
Phosphorus fractions and related properties in soils under Pinus sylvestris L. plantations in Spain
<p>This database presents information about the P fractions in soils determined following the method developed by Hedley et al. (1982) and modified by Tiessen and Moir (1993) and other soil chemical properties of soils under <em>Pinus sylvestris </em>L. plantations in Spain.</p> <p>Abbreviations of variables names and units are described below:</p> <p>pH: soil pH; EOC: easily oxidizable C (%); EA: exchangeable acidity (cmol<sub>(+)</sub>·kg<sup>-1</sup>); Ca: exchangeable Ca (cmol<sub>(+)</sub>·kg<sup>-1</sup>); Sat: base saturation of the exchangeable complex (%); Al<sub>A</sub>, Fe<sub>A</sub>: amorphous Al and Fe (mg kg<sup>-1</sup>); Al<sub>E</sub>: exchangeable Al (cmol<sub>(+)</sub>·kg<sup>-1</sup>); Al<sub>M</sub>, Fe<sub>M</sub>: organically bound Al and Fe (mg kg<sup>-1</sup>); SI: forest site index (m); Cmic: microbial biomass C (mg kg<sup>-1</sup>); Pmic: microbial biomass P (mg kg<sup>-1</sup>); Cmin: mineralizable C (mg·kg<sup>-1</sup>·week<sup>-1</sup>) ; AcPhos: acid phosphatase activity (µg·g<sup>-1</sup>·h<sup>-1</sup>); PAEM: available P (mg kg<sup>-1</sup>); PiNaHCO3, PoNaHCO3: inorganic and organic highly labile P (mg kg<sup>-1</sup>); PoNaOH; PiNaOH: inorganic and organic moderately labile P (mg kg<sup>-1</sup>); PHCl1M: primary P (mg kg<sup>-1</sup>); PHClconc: stable P (mg kg<sup>-1</sup>); PHClO4: residual P (mg kg<sup>-1</sup>); PTotal: addition of all previous P fractions analysed (mg kg<sup>-1</sup>).</p>
Raw data for: Habitat edges affect tree diversity more than biomass regeneration in a reforested wet neotropical timber plantation
<p>Raw data for: Habitat edges affect tree diversity more than biomass regeneration in a reforested wet neotropical timber plantation. Code hosted on GitHub/Zenodo.</p>
Figs 9–16 in First record of the genus Bloszykiella in Kenya with the description of Bloszykiella tertia sp. n. (Acari: Uropodidae) from a Pinus radiata D. Don plantation
Figs 9–16. Bloszykiella tertia sp. n., female, holotype, Kenya: (9) tritosternum; (10) entral view of gnathosoma and palp; (11) apical part of epistome; (12) chelicerae; (13) Leg I; (14) Leg II; (15) Leg III; (16) Leg IV (all legs in ventral view, claw of Leg IV not illustrated).
Figs 1–4 in First record of the genus Bloszykiella in Kenya with the description of Bloszykiella tertia sp. n. (Acari: Uropodidae) from a Pinus radiata D. Don plantation
Figs 1–4. Bloszykiella tertia sp. n., female, holotype, Kenya: (1) dorsal view of body; (2) ornamentation and setae on dorsal shield; (3) caudal area of dorsal idiosoma; (4) ventral view of body.
Figs 5–8 in First record of the genus Bloszykiella in Kenya with the description of Bloszykiella tertia sp. n. (Acari: Uropodidae) from a Pinus radiata D. Don plantation
Figs 5–8. Bloszykiella tertia sp. n., female, holotype, Kenya: (5) lateral part of ventral shield with ventral setae; (6) anal area of ventral shield; (7) intercoxal area; (8) peritreme.
Data from: Rainforest conversion to plantations fundamentally alters energy fluxes and functions in canopy arthropod food webs
<p><span>Tropical rainforests around the world are rapidly being converted into cash-crop agricultural systems. The associated massive losses of plant and animal species lead to changes in arthropod food webs and the energy fluxes therein. These changes are poorly understood, in particular in the extremely biodiverse canopies of tropical ecosystems. Using canopy fogging followed by stable isotope and energy flux analyses, we show that land-use conversion from rainforest to rubber and oil palm plantations not only causes a drastic reduction in energy fluxes of up to 75% but also shifts fluxes among trophic groups. While rainforests featured high levels of both herbivory and algae-microbiology, and a balanced ratio of herbivory to predation, relative fluxes were shifted towards predation in rubber and towards herbivory in oil palm plantations, indicating profound shifts in ecosystem functioning. Our results highlight that the ongoing loss of animal biodiversity and biomass in tropical canopies degrades animal-driven functions and restructures canopy food webs.</span></p>
Fig. 1 in Giant rhinoceros beetle Golofa claviger (Linnaeus) (Coleoptera: Melolonthidae: Dynastini) is damaging North Brazilian oil palm plantations
Fig. 1. Golofa claviger on oil palm. A – specimens collected in the infested area; B – dead males of G. claviger sheltered on the rachis or stem angles of the young palm; C – adult male lying on a palm leaflet; D – ripped young frond; E and F – wedge-shaped cuts on young, not yet unfurled frond; G – ripped unfurled frond.
Data from: Are tree plantations promoting homogenization of mammal assemblages between regions with contrasting environments?
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Data from: Rainforest conversion to plantations fundamentally alters energy fluxes and functions in canopy arthropod food webs
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Data from: Native shade trees aid bird conservation in tea plantations in southern India
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Data from: Shifting agriculture supports more tropical forest birds than oil palm or teak plantations in Mizoram, northeast India
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Tree carbon fluxes and stocks in West African cocoa plantations
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