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304 results for “eucalyptus”
Fig. 1 in Environmental determinants affecting the occurrence of defoliator caterpillars on Eucalyptus (Myrtaceae) plantations in the Brazilian Amazonian region
Fig. 1. Number of Oxydia vesulia (Lepidoptera: Geometridae) and Sarsina violascens (Lepidoptera: Lymantriidae) adults collected with light traps in Eucalyptus urophylla (Myrtaceae) plantations as a function of the number of rotations of this plant in the same area. (Almeirim Municipality, Pará State, and Laranjal do Jari Municipality, Amapá State, Brazil).
Fig. 5 in Dispersal of the zoophytophagous predator Brontocoris tabidus and Podisus nigrispinus (Heteroptera: Pentatomidae) in an eucalyptus plantation
Fig. 5. Distribution of the predators Brontocoris tabidus and Podisus nigrispinus (Heteroptera: Pentatomidae) males and females in a clonal eucalyptus plantation (Eucalyptus grandis × Eucalyptus urophylla) 7 d afer release.
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.
Eucalyptus cladocalyx wood formation
<p>The dataset comprises transverse sections of <em>Eucalyptus cladocalyx</em> stem tissue, highlighting various cell types such as vessels, fibers, and cambium after exposure to cyclic drought treatments. Stem samples were embedded in paraffin wax, sectioned at a thickness of 6 µm, and stained using Safranin-Alcian blue. Microscopic images were captured using a Nikon Eclipse Ni-E upright motorized microscope equipped with NIS-Elements D software, with a 20X objective lens providing a resolution of 0.24 µm/pixel in 24-bit RGB color.</p>
Figures 14–17 in Two new Australian species of Stethynium (Hymenoptera: Mymaridae), larval parasitoids of Ophelimus maskelli (Ashmead) (Hymenoptera: Eulophidae) on Eucalyptus
Figures 14–17. Stethynium breviovipositor, male. (14) Antenna. (15) Mesosoma and metasoma, dorsal. (16) Mesosoma and metasoma, lateral. (17) Genitalia, lateral.
Figures 4–7 in Two new Australian species of Stethynium (Hymenoptera: Mymaridae), larval parasitoids of Ophelimus maskelli (Ashmead) (Hymenoptera: Eulophidae) on Eucalyptus
Figures 4–7. Stethynium ophelimi. (4) Female body, lateral. (5) Holotype, head, anterior, and antenna. (6) Male head and antenna. (7) Male mesosoma and metasoma, dorsal.
Figures 1–3 in Two new Australian species of Stethynium (Hymenoptera: Mymaridae), larval parasitoids of Ophelimus maskelli (Ashmead) (Hymenoptera: Eulophidae) on Eucalyptus
Figures 1–3. Stethynium ophelimi sp. n., female. (1) Wings. (2) Antenna. (3) Holotype, mesosoma+metasoma, dorsal.
Figures 10–13 in Two new Australian species of Stethynium (Hymenoptera: Mymaridae), larval parasitoids of Ophelimus maskelli (Ashmead) (Hymenoptera: Eulophidae) on Eucalyptus
Figures 10–13. Stethynium breviovipositor, female. (10) Antenna. (11) Mesosoma and metasoma, dorsal. (12) Body, lateral. (13) Head, anterior.
Figures 8, 9 in Two new Australian species of Stethynium (Hymenoptera: Mymaridae), larval parasitoids of Ophelimus maskelli (Ashmead) (Hymenoptera: Eulophidae) on Eucalyptus
Figures 8, 9. Stethynium spp. (8) S. ophelimi, male genitalia, dorsal. (9) S. breviovipositor sp. n., wings.
Figures 18, 19 in Two new Australian species of Stethynium (Hymenoptera: Mymaridae), larval parasitoids of Ophelimus maskelli (Ashmead) (Hymenoptera: Eulophidae) on Eucalyptus
Figures 18, 19. (18) Leaf of Eucalyptus camaldulensis with heavy infestation of Ophelimus maskelli galls. (19) Leaf of E. camaldulensis showing four intact O. maskelli galls, two galls with emergence holes (bottom right), and two dissected galls (left), one of which contains an unemerged adult Stethynium sp. (arrow).
Plant management but not fertilization mediates soil carbon emission and microbial community composition in subtropical Eucalyptus plantations
Open the record for dataset details and reuse information.
Aplication of eco-enzyme from nutmeg, clove, and eucalyptus plant waste in inhibiting the growth of E. coli and S. aureus
<p>That different plant wastes' eco-enzymes also had distinctive colors, where DP and DK were brown, BP was reddish-brown, while DC appeared blackish-brown and clear. These differences occur due to variations in the chemical composition of each material used. Furthermore, the acidic aroma from each eco-enzyme was derived from the decomposition of alcohol compounds into acetic acid during aerobic respiration. The aroma was distinctively different depending on the type of plant waste used. Eco-enzymes and commercial antiseptics also have different abilities to inhibit <em>E. coli</em> and <em>S. aureus </em>growth with the highest inhibition found in eco-enzymes made from eucalyptus leaf waste</p>
Figure 3 in Bird-plant interaction networks in native forests and eucalyptus plantations within a protected area
Figure 3. Comparison of the number of interactions between frugivorous birds and plants between native forest and eucalyptus plantation in the PEIT. (a): Fecal samples interactions (P-value = 0.83, W = 3.5); (b): Focal observation interactions (P-value = 0.99, W = 4.0).
Figure 2 in Bird-plant interaction networks in native forests and eucalyptus plantations within a protected area
Figure 2. Interaction networks between frugivorous birds and zoochoric plants, according to the focal observations of birds in both sampled habitats. The circles represent the plant species, and the species of birds are represented by triangles. The acronyms in the center of the figures are the scientific names of the species (Supplementary material 1). The thickness of the links (lines) is related to the connectivity between each species (the thicker the line, the more records this interaction had). Each color represents a cluster of species that are more connected within each other than with between species from other clusters due to its modularity (Q). (a): Fragments of native forest; (b): Fragments of eucalyptus plantation.
Figure 1 in Bird-plant interaction networks in native forests and eucalyptus plantations within a protected area
Figure 1. Interaction networks between frugivorous birds and zoochoric plants, according to the fecal samples of birds in the understory of the two sampled habitats. The circles represent the plant species, and the triangles are representing the species of birds. The acronyms in the center of the figures are the scientific names of the species (Supplementary material 1). The thickness of the links (lines) is related to the connectivity between each species (the thicker the line, the more records this interaction had). Each color represents a cluster of species that are more connected within each other than with species from other clusters due to its modularity (Q). (a): F fragments of native forest; (b): Fragments of eucalyptus plantation.
Figure 1 in The stem borer Zeuzera multistrigata Moore (Lepidoptera, Cossidae): a serious pest undermining Eucalyptus plantations in Northern Vietnam
Figure 1. Distribution of Zeuzera multistrigata in Eucalyptus plantations in Northern Vietnam.
DaRT-seq raw data of Eucalyptus spp for the genetic assessment of the value of restoration planting within an endangered eucalypt woodland
<p>Assessment of woodland restoration often focusses on stand demographics, but genetic factors likely influence long-term stand viability. We examined the genetic composition of Yellow Box (<em>Eucalyptus melliodora</em>) trees in endangered Box-Gum Grassy Woodland in SE Australia, some 30 years after planting with seeds of reportedly local provenance. Using DArT sequencing for 1406 SNPs, we compared genetic diversity and population structure of planted <em>E. melliodora</em> trees with remnant bushland trees, paddock trees, and natural recruits. Genetic patterns imply that natural stands and paddock trees had historically high gene flow (among group pairwise FST = 0.04–0.10). Genetic diversity was highest among relictual paddock trees (He = 0.17), while diversity of revegetated trees was identical to natural bushland trees (He = 0.14). Bayesian clustering placed the revegetated trees into six genetic groups with four corresponding to genotypes from paddock trees, indicating that revegetated stands are mainly of genetically diverse, local provenance. Natural recruits were largely derived from paddock trees with some contribution from planted trees. A few trees have likely hybridised with other local eucalypt species which are unlikely to compromise stand integrity. We show that paddock trees have high genetic diversity and capture historic genetic variety and provide important foci for natural recruitment of genetically diverse and outcrossed seedlings.</p>
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