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146 results for “saproxylic”
Saproxylic Organisms
Trait data for saproxylic organisms textmined through Natural Language Processing of the Biodiversity Heritage Library corpus.
Figure 1 in Deadwood and saproxylic beetle diversity in naturally disturbed and managed spruce forests in Nova Scotia
Figure 1. Non-metric multidimensional scaling ordination diagrams of forest sites in two-dimensional space defined by (A) beetle assemblage and (B) habitat structures. Symbols signify disturbance history class of forests: 1= CLEARCUT, D= THINNED, ·= FIRE, and Ɨ= WIND. Numbers identify the specific forest. Forest number 25 was excluded as an outlier in (B) due to much higher deadwood volumes than all other sites.
Fig. 1 in Saproxylic beetle (Coleoptera) communities and forest management practices in coniferous stands in southwest Nova Scotia, Canada
Fig. 1. Map of Bowater Mersey Paper Company Ltd land in Nova Scotia. Bowater Mersey lands highlighted. Site descriptions: 1 & 2 – 40-80 yr, CT; 3 & 4 – 40-80 yr, none; 5 – 80-120 yr, US; 6 & 7 – 80- 120, none; 8 – 120+ yr, S; 9 – 120+ yr, S/SH; 10 & 11 – 120+ yr, none. CT = Commercial thinning; US = Uniform selection harvest; SH = Shelterwood harvest; S = Selection harvest.
Fig. 2 in Saproxylic beetle (Coleoptera) communities and forest management practices in coniferous stands in southwest Nova Scotia, Canada
Fig. 2. Overstory composition for dominant tree species based on importance value (Importance Value = Relative Density + Relative Dominance + Relative Frequency). Site descriptions: 1 & 2 – 40-80 yr, CT; 3 & 4 – 40-80 yr, none; 5 – 80-120 yr, US; 6 & 7 – 80-120, none; 8 – 120+ yr, S; 9 – 120+ yr, S/SH; 10 & 11 – 120+ yr, none. CT = Commercial thinning; US = Uniform selection harvest; SH = Shelterwood harvest; S = Selection harvest.
Fig. 7 in Saproxylic beetle (Coleoptera) communities and forest management practices in coniferous stands in southwest Nova Scotia, Canada
Fig. 7. Mean species richness of beetles in different forest stand age classes, including standard deviation from both the present study and Bishop (1998).
Fig. 5 in Saproxylic beetle (Coleoptera) communities and forest management practices in coniferous stands in southwest Nova Scotia, Canada
Fig. 5. Rarefaction curve demonstrating projected species richness for number of individuals based on Bishop (1998), and the present study (Dollin et al.) beetle collections.
Fig. 8 in Saproxylic beetle (Coleoptera) communities and forest management practices in coniferous stands in southwest Nova Scotia, Canada
Fig. 8. Mean species richness across harvest treatment, including standard deviation, for 11 stands in southwestern Nova Scotia.
Fig. 3 in Saproxylic beetle (Coleoptera) communities and forest management practices in coniferous stands in southwest Nova Scotia, Canada
Fig. 3. Volume of coarse woody debris (CWD) by decay class for 11 stands in southwestern Nova Scotia as measured by Thompson (2004). Decay classes are summarized as follows: "1" is freshly dead, little to no rot; in "2", the bole is mostly sound; "3" has well-established rot and significant bark loss; "4" is advanced decay; and "5" is rotted through but still of wood character. Site descriptions: 1 & 2 – 40-80 yr, CT; 3 & 4 – 40-80 yr, none; 5 – 80-120 yr, US; 6 & 7 – 80-120, none; 8 – 120+ yr, S; 9 – 120+ yr, S/SH; 10 & 11 – 120+ yr, none. CT = Commercial thinning; US = Uniform selection harvest; SH = Shelterwood harvest; S = Selection harvest.
Fig.1 in A Review Of Latvian Saproxylic Beetles From The European Red List
Fig.1. Red List Categories taken from International Union for Conservation of Nature (IUCN) (Nieto & Alexander 2010).
Fig. 2 in Saproxylic weevils and edaphic beetles as indicators of environmental quality of relict forests in Piedmont lowlands (Coleoptera)
Fig. 2 – Map of Parco della Partecipanza, completely surrounded by agroecosystems. Map data: Google Earth, Maxar Technologies, used according to Google Earth Terms of Service.
Fig. 1 in Saproxylic weevils and edaphic beetles as indicators of environmental quality of relict forests in Piedmont lowlands (Coleoptera)
Fig. 1 – The collecting sites. Map data: Google Earth, Maxar Technologies, used according to Google Earth Terms of Service.
Fig. 5 in Saproxylic weevils and edaphic beetles as indicators of environmental quality of relict forests in Piedmont lowlands (Coleoptera)
Fig. 5 – Some of the weevils collected in the research. a, Kyklioacalles navieresi (Boheman, 1837); b, Kyklioacalles aubei (Boheman, 1837); c, Acalles echinatus (Germar, 1824); d, Echinodera hypocrita (Boheman, 1837). From Stüben (2014-2020), used with permission.
Fig. 2 in First exact data on the distribution of saproxylic species Calchaenesthes oblongomaculata (Guérin- Méneville, 1844) (Cerambycidae: Purpuricenini) in Bulgaria
Fig. 2. Collecting site in Maleshevska Planina Mts. A: General view of the habitat. B: Flowering Quercus pubescens tree.
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.
Linked collectors and determiners for: Collection of saproxylic and xylobiont Beetles.
Natural history specimen data linked to collectors and determiners held within, "Collection of saproxylic and xylobiont Beetles". Claims or attributions were made on Bionomia by volunteer Scribes, <a href="https://bionomia.net/dataset/d3d38190-0c13-11df-b8c6-b8a03c50a862">https://bionomia.net/dataset/d3d38190-0c13-11df-b8c6-b8a03c50a862</a> using specimen data from the dataset aggregated by the Global Biodiversity Information Facility, <a href="https://gbif.org/dataset/d3d38190-0c13-11df-b8c6-b8a03c50a862">https://gbif.org/dataset/d3d38190-0c13-11df-b8c6-b8a03c50a862</a>. Formatted as a Frictionless Data package.
Figure 7 in The early stages and breeding sites of four rare saproxylic hoverflies (Diptera: Syrphidae) from Spain
Figure 7. Typical Mallota-shaped puparium of M. dusmeti, lacking the detachable thoracic plate and the drawomitted long tail in lateral view, with head to the left. Scale bar: 4 mm.
Figures 8, 9 in The early stages and breeding sites of four rare saproxylic hoverflies (Diptera: Syrphidae) from Spain
Figures 8, 9. Head skeletons in lateral view. (8) Mallota dusmeti. (9) Myolepta difformis. Scale bar: 1.2 mm.
Figures 3–6 in The early stages and breeding sites of four rare saproxylic hoverflies (Diptera: Syrphidae) from Spain
Figures 3–6. Closely related Ferdinandea species posterior respiratory processes (prp) showing the tube sculpture and the spiracular plate, in dorsal and apical views, respectively. (3, 4) Ferdinandea cuprea. (5, 6) Ferdinandea fumipennis. Scale bars: 1 mm.
Figures 1, 2 in The early stages and breeding sites of four rare saproxylic hoverflies (Diptera: Syrphidae) from Spain
Figures 1, 2. Mandibular sclerite detail from closely related Ferdinandea species head skeletons in lateral view. (1) Ferdinandea cuprea. (2) Ferdinandea fumipennis. Scale bar: 1 mm.
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