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42 results for “wood-boring”
FIG. 5 in At the bottom of the deep blue sea: a new wood-boring bivalve (Mollusca, Pholadidae, Xylophaga) from the Cape Verde Abyssal Plain (subtropical Atlantic)
FIG. 5. — Incurrent siphonal opening of Xylophaga alexisi n. sp., SEM. Note absence of cirri. Scale bar: 30 µm.
FIG. 4 in At the bottom of the deep blue sea: a new wood-boring bivalve (Mollusca, Pholadidae, Xylophaga) from the Cape Verde Abyssal Plain (subtropical Atlantic)
FIG. 4. — Excurrent siphonal opening of Xylophaga alexisi n. sp., SEM: A, lateral view; B, dorsal view. Scale bars: A, 10 µm; B, 100 µm.
FIG. 2. — A in At the bottom of the deep blue sea: a new wood-boring bivalve (Mollusca, Pholadidae, Xylophaga) from the Cape Verde Abyssal Plain (subtropical Atlantic)
FIG. 2. — A, lateral view of an intact specimen of Xylophaga alexisi n. sp.; B, dorsal view of intact, larger specimen of X. alexisi n. sp. (note anteriorly directed mesoplax); C, dorsal view of smaller specimen of X. alexisi n. sp., mesoplax in erect stage, not readily seen from dorsal view. Scale bars: 1 mm.
FIG. 1. — A in At the bottom of the deep blue sea: a new wood-boring bivalve (Mollusca, Pholadidae, Xylophaga) from the Cape Verde Abyssal Plain (subtropical Atlantic)
FIG. 1. — A, collection locality of Xylophaga alexisi n. sp. at 21°N, 30°W; R, collection locality of Xylophaga ricei Harvey, 1996 at 31°N, 20°W. (From Ryan et al. 2009, modified by Y. Lagabrielle.)
FIG. 6. — A, Xylophaga alexisi n in At the bottom of the deep blue sea: a new wood-boring bivalve (Mollusca, Pholadidae, Xylophaga) from the Cape Verde Abyssal Plain (subtropical Atlantic)
FIG. 6. — A, Xylophaga alexisi n. sp., lateral view to define "incomplete siphon" in which the excurrent siphon is considerably shorter than the incurrent siphon; B, Xylophaga pacifica Voight, 2009, lateral view to define "complete siphon", in which both siphonal openings are roughly equal in length. Scale bars: 1 mm.
Data from: Size matters: when resource accessibility by ecosystem engineering elicits wood-boring beetle demographic responses
<p>This data was used to investigate how the age and size of beaver disturbances act as predictors for primary wood-boring beetle abundance and species richness around beaver-altered habitat patches. To do so, we sampled beetles around 16 beaver-disturbed and unaltered watercourses within the Kouchibouguac National Park (Canada) and modeled beetle demographical responses to site conditions and their physical characteristics, distance from the watercourse, deadwood biomass, and the geographical location of the sites.</p>
Data from: Size matters: when resource accessibility by ecosystem engineering elicits wood-boring beetle demographic responses
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Metagenomic and genomic data of symbiotic bacteria from wood-boring shipworms <em>Lyrodus pedicellatus</em> and <em>Teredo bartschi</em>
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Assessment of the systems approach for the phytosanitary treatment of wood infested with wood-boring insects
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Determination of the Damage Severity of Wood-Boring Beetles According to the Bevan Damage Classification System
<p>The aim of the study was to determine damage severity of wood-destroying insects on logs stored in forest depots. The Bevan damage classification (BDC) system, developed in 1987, was utilized to determine damage severity in log depots in 21 locations throughout seven provinces in Turkey. Pheromone traps were placed in those locations at the beginning of April in 2015 and 2016. Furthermore some stored wood within the log depots were checked and split into small pieces to collect insects that damage wood. The BDC system was used for the first time to measure the severity of insect damage in log depots. Twenty-eight families, 104 genera and 123 species were identified in this study. Based on the BDC system, the highest damage was found from the Cerambycidae and Buprestidae families. <em>Arhopalus rusticus</em> was determined as the insect responsible for the highest amount of damage with 8.8% severity rating in the pheromone-trapped insects group. When the stored wood material was considered, <em>Hylotrupes bajulus</em> was found to be the cause of the highest damage. The lowest damage values were among the predator insects (Cleridae, Trogossitidae, Cantharidae) and those feeding on fungi colonized on the wood (Mordellidae, Cerylonidae, Nitidulidae). Some other predator insects of the Tenebrionidae family (<em>Uloma cypraea, Uloma culinaris, Menephilus cylindricus</em>) and Elateridae family (<em>Lacon punctatus</em>, <em>Ampedus</em> sp.) exhibited relatively higher damage severity values since they had built tunnels and made holes in the stored wood material. When the environmental factors were considered, the Buprestidae family exhibited a very strong positive relationship (<em>p</em> <0.005) with insect frequency distribution (r = 0.922), number of species (r = 0.879) and insect density (r = 0.942). Both families showed the highest number and frequency during July and August, highlighting the importance of insect control and management during these months.</p>
FIGURE 2. Micromalthus debilis LeConte, 1878 in Micromalthus debilis LeConte, 1878 (Coleoptera: Micromalthidae), an American wood-boring beetle new to Italy
FIGURE 2. Micromalthus debilis LeConte, 1878, distribution. Green ellipse: area of origin; red dots: record in the literature; orange triangle: first breeding record in Europe (Trieste, Italy).
FIGURES 55–59. 55 in The world species of Balcha Walker (Hymenoptera: Chalcidoidea: Eupelmidae), parasitoids of wood-boring beetles
FIGURES 55–59. 55. Balcha enoptra: syntergum. 56 and 57. B. punctiscutum: 56, syntergum; 57, base of syntergum. 58 and 59. B. camptogastra: 58, lateral habitus; 59, syntergum.
FIGURES 9–18 in The world species of Balcha Walker (Hymenoptera: Chalcidoidea: Eupelmidae), parasitoids of wood-boring beetles
FIGURES 9–18. Mesosoma dorsal: 9, Balcha laciniosa; 10, B. cylindrica; 11, B. elegans; 12, B. indica (N. Am.); 13, B. eximia; 14, B. eximiassita; 15, B. dictyota; 16, B. reticulata; 17, B. anemeta; 18, B. splendida (nob = notaular band, pnb = paranotaular band, ppb = parapsidal band).
FIGURES 47–54. 47 in The world species of Balcha Walker (Hymenoptera: Chalcidoidea: Eupelmidae), parasitoids of wood-boring beetles
FIGURES 47–54. 47. Metanotum and propodeum: Balcha eximia. 48. B. indica (N. Am.): dorsellum and propodeal plical region. 49 and 50. Mesosoma, lateral: 49, B. punctiscutum; 50, B. indica (N. Am.). 51–54. Posterior half of acropleuron: 51, B. indica (holotype); 52, B. eximiassita; 53, B. anemeta; 54, B. levicollis (sar = subalar region of acropleuron).
FIGURES 39–46. 39–42 in The world species of Balcha Walker (Hymenoptera: Chalcidoidea: Eupelmidae), parasitoids of wood-boring beetles
FIGURES 39–46. 39–42. Mesosoma, dorsal: 39, Balcha cylindrica; 40, B. splendida; 41, B. camptogastra; 42, B. enoptra. 43–46. Metanotum and propodeum: 43, B. levicollis; 44, B. punctiscutum; 45, B. enoptra (cal = callus, dor = dorsellum, pcr = precrenular region of metanotal panel, ppr = propodeal plical region, psr = paraspiracular region); 46, B. elegans.
FIGURES 31–38 in The world species of Balcha Walker (Hymenoptera: Chalcidoidea: Eupelmidae), parasitoids of wood-boring beetles
FIGURES 31–38. Mesosoma dorsal: 31, Balcha anemeta; 32, B. punctiscutum; 33, B. indica (N. Am.); 34, B. indica (holotype); 35, B. elegans; 36, B. laciniosa (not = notaulus, pl = parapsidal line); 37, B. eximiassita; 38, B. reticulata.
Alpha-diversity, Beta-diversity and host-specificity of wood-boring longhorn beetle (Cerambycidea) in Asian tropical and subtropical forests
<p><span>A long-debated question in ecology is whether the hyper-diversity of tropical plant-feeding insects is a direct consequence of high tropical plant diversity and/or should be attributed to increases in host plant specialization. To address this debate, we used the longhorn beetle as a study system because their larval stages feed on the xylems of trees and lianas. We hypothesized that longhorn beetles show higher host-specificity in tropical forests than in other forests; alternatively, the high longhorn beetle diversity in the tropics may simply be owing to more diverse host plants. We therefore designed an investigation in tropical and subtropical forests to test these hypotheses. We adapted several analyses (i.e., non-metric multidimensional scaling analysis, alpha-diversity, beta-dissimilarity indices comparisons, and variation partitioning based on redundancy analysis) to compare the species diversity of plants and longhorn beetles in different forests. Our results show that both the plant and beetle species in the tropical and subtropical areas were well-stratified (non-metric multidimensional scaling analysis). The beetle alpha-diversity in the tropical forests was significantly higher than that in the subtropical forests, but the plant alpha-diversity in the two types of forests were not significantly different. The beta-dissimilarity comparison showed that the plant species exerted a significant influence on beetle compositional assemblage in the tropical forests, but not in the subtropical forests. Finally, the variation partitioning results showed that both plant species and plant phylogenetic beta-diversity possessed significant explanatory power for beetle assemblage composition in the tropical forests, but not in the subtropical forests. We conclude that wood-boring longhorn beetles show higher host-specificity in tropical forests than in subtropical forests, and the high diversity of wood-boring longhorn beetles in tropical forests might be explained to a large extent by their more finely partitioned diet-breadth.</span></p>
FIGURE 3 in Wood-boring limnoriids (Crustacea, Isopoda) including a new species from mangrove forests of the Tukang Besi Archipelago, Indonesia
FIGURE 3. Lateral views of limnoriids from the Tukang Besi mangrove forests. A, Limnoria sellifera sp. nov.; B, Limnoria insulae; C, Limnoria unicornis; D, Limnoria pfefferi. Backscatter detector SEM images. Scale bars = 200 µm.
FIGURE 4 in Wood-boring limnoriids (Crustacea, Isopoda) including a new species from mangrove forests of the Tukang Besi Archipelago, Indonesia
FIGURE 4. Oblique dorsal views of pleonites and pleotelson. A, Limnoria sellifera sp. nov.; B, Limnoria pfefferi (note lorica of folliculinid on the right hand side of the pleotelson); C, Limnoria insulae; D, Limnoria unicornis. Backscatter detector SEM images. Scale bars = 100 µm in A and D, and 200 µm in B and C.
FIGURE 7. Uropods. A in Wood-boring limnoriids (Crustacea, Isopoda) including a new species from mangrove forests of the Tukang Besi Archipelago, Indonesia
FIGURE 7. Uropods. A, Limnoria sellifera sp. nov., lateral view; B, Limnoria unicornis, lateral view; C, Limnoria pfefferi; D, Limnoria insulae, oblique ventral view. Backscatter detector SEM images. Scale bars indicate 50, 50, 100 and 200 µm for A, B, C and D respectively.
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