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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.

opencc-by-4.0Dec 2022View details →

Figure 5 in Composition and structure of plant communities in the Moist Temperate Forest Ecosystem of the Hindukush Mountains, Pakistan

Figure 5. CCA plot Analysis of illustrating the influence of elevation on spreading pattern of plant communities in Lalkoo valley Swat.

opencc-by-4.0Dec 2022View details →

Figure 4 in Composition and structure of plant communities in the Moist Temperate Forest Ecosystem of the Hindukush Mountains, Pakistan

Figure 4. Results of CCA joint biplot showing results for eleven plant communities' correlation with environmental variable. BAB-I: Berberis- Abies- Bergenia; PIP-II: Picea-Indigofera- Poa; APP-III: Abies- Parrotiopsis- Poa,QVP-IV:Quercus-Viburnum-Poa,PSP-V:PiceaSalix-Primula,AVP-VI:Abies-Viburnum -Poa; VTP-VII: ViburnumTaxus-Poa; PVL-VIII: Pinus-Viburnum-Lithospermum; ABC-IX: Abies-Berberis-Carex; PVP-X: Pinus-Viburnum-Poa; and PPP-XI: Parrotiopsis-Picea-Poa represents community types.

opencc-by-4.0Jul 2024View details →

Cycles in hydrologic intensification and de-intensification create instabilities in spring nitrate-N export C-Q behavior in northern temperate forests

Data supporting analysis in "Cycles in hydrologic intensification and de-intensification create instabilities in spring nitrate-N export C-Q behavior in northern temperate forests". The worksheet "daily SWE" contains modeled daily snow water equivalent (SWE; mm) at Turkey Lakes Watershed.  Daily values were modeled using a snow accumulation and melt routine within a hydrologic model that used measured precipitation and snow survey data as input and was calibrated to daily discharge measurements at a reference catchment.  For use of SWE data, please cite: Leach, J. A., Buttle, J. M., Webster, K. L., Hazlett, P. W., & Jeffries, D. S. (2020). Travel times for snowmelt-dominated headwater catchments: influences of wetlands and forest harvesting, and linkages to stream water quality. Hydrological Processes, 34(10), 2154-2175. https://doi.org/10.1002/hyp.13746 The worksheet "monthly T, P, PET" contains monthly mean temperature (°C), monthly total precipitation (mm), and monthly Hamon potential evapotranspiration (PET; mm) from measurements made at the Algoma CAPMoN (Canadian Air and Precipitation Monitoring Network) meteorological station (47°02′N, 84°22′W, 411 m.a.s.l.). For use of these climate data, please cite: Semkin, R. G., Jeffries, D. S., Neureuther, R., Lahaie, G., McAulay, M., Norouzian, F., & Franklyn, J. (2012). Summary of hydrological and meteorological measurements in the Turkey Lakes Watershed, Algoma, Ontario, 1980-2010. Water Science and Technology Directorate Contribution No. 11-145. Environment Canada, National Water Research Institute, Burlington, ON, 85 p.

Figure 6. A-B in Two new species of Anaulacodesmus Attems, 1898 (Polydesmida: Dalodesmidae) from temperate forest fragments in southern Chile

Figure 6. A-B. Gonopods of Anaulacodesmus picassovallebuonai sp. nov. (not to scale). A. posterior view. B. Anterior view. / A-B. Gonópodos de Anaulacodesmus picassovallebuonai sp. nov. (no tomado a escala). A. vista posterior. B. Vista anterior.

Figure 3. A-C in Two new species of Anaulacodesmus Attems, 1898 (Polydesmida: Dalodesmidae) from temperate forest fragments in southern Chile

Figure 3. A-C. Gonopods of Anaulacodesmus panterae sp. nov. (not to scale). A. Posterior view. B. Lateral view. C. Anterior view. Base of right gonopod slightly damage with a transversal cut. / A-C. Gonópodos de Anaulacodesmus panterae sp. nov. (no tomado a escala). A. Vista posterior. B. Vista lateral. C. Vista anterior. Base del gonópodo derecho levemente dañada con un corte transversal.

Figure 1 in Two new species of Anaulacodesmus Attems, 1898 (Polydesmida: Dalodesmidae) from temperate forest fragments in southern Chile

Figure 1. Anaulacodesmus panterae sp. nov., paratypes, lateral view, top: female, bottom: male. Scale: 4.0 mm. / Anaulacodesmus panterae sp. nov., paratipos, vista lateral, arriba: hembra, abajo: macho. Escala: 4,0 mm.

Figure 2 in Two new species of Anaulacodesmus Attems, 1898 (Polydesmida: Dalodesmidae) from temperate forest fragments in southern Chile

Figure 2. Anaulacodesmus panterae sp. nov. A. Habitat. B-C. Habitus. / Anaulacodesmus panterae sp. nov. A. Hábitat. B-C. Hábito.

Figure 5 in To what extent do pine and oak clear-cut stumps support mite (Acari: Mesostigmata) communities in temperate forests?

Figure 5. Proportional abundance of dominant mite species in CWD and adjacent litter in Scots pine (A) and sessile oak (B) forest.

Figure 6 in To what extent do pine and oak clear-cut stumps support mite (Acari: Mesostigmata) communities in temperate forests?

Figure 6. DCA biplot species data for the different microhabitat of the forest floor. Microhabitat are marked as: tree species [SP - Scots pine and SO - sessile oak] and 5 microhabitat types: [(CWD - coarse woody debris, ecotone, and litter at distances of 0.5, 1.0, and 1.5 m)].

Figure 3 in To what extent do pine and oak clear-cut stumps support mite (Acari: Mesostigmata) communities in temperate forests?

Figure 3. Species accumulation curves (A, B) and proportional abundance (C, D) of Gamasina and Uropodina in litter/soil and CWD (stumps) in Scots pine and sessile oak forest.

Figure 1 in To what extent do pine and oak clear-cut stumps support mite (Acari: Mesostigmata) communities in temperate forests?

Figure 1. Sampling design in sessile oak and Scots pine forest. The oak and pine stumps were sampled in three directions from five microhabitats.

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Figures 1–9 in Armored scales (Hemiptera: Diaspididae) from warm temperate forests in Korea

Figures 1–9. Species of armored scales new to Korea.1–2: Andaspis recurrens, 1) female, 2) pygidium. 3–4: Hypaspidiotus jordani, 3) female, 4) pygidium. 5–7: Lepidosaphes kamakurensis, 5) habitus, 6) female, 7) pygidium. 8–9: Selenomphalus distylii, 8) female, 9) pygidium.

Fig. A3 in Susceptibility of tropical mountain forests to biological invasions from the temperate and subtropical zone, exemplified by Zonitoides (Gastropoda: Gastrodontidae)

Fig. A3. Map of the occurrences of Zonitoides arboreus s.l. and Zonitoides nitidus used for the calculation of climatic suitability for the 20 km grid resolution.

Fig. A4 in Susceptibility of tropical mountain forests to biological invasions from the temperate and subtropical zone, exemplified by Zonitoides (Gastropoda: Gastrodontidae)

Fig. A4. Global climatic suitability for: (a) Zonitoides arboreus s.l.; and (b) Zonitoides nitidus based on Mahalanobis distances using the 20 km grid resolution. The higher the threshold, the more dissimilar are the climatic conditions to those of the majority of known occurrences, and>100% means that the climatic conditions are dissimilar to those of any other available record. Please note that the deserts of Africa, Arabia and Australia are unlikely places for a snail that inhabits (temperate) forests in its native range (Z. arboreus s.l.), and that the Great Lakes Region that seems well inhabited by Z. nitidus does not fully match its climate, what can only be explained from effects of averaging local climates at a larger grid scale.

Fig. A1 in Susceptibility of tropical mountain forests to biological invasions from the temperate and subtropical zone, exemplified by Zonitoides (Gastropoda: Gastrodontidae)

Fig. A1. Map of the occurrences of Zonitoides arboreus s.l. used for the calculation of climatic suitability for the 10 km grid resolution.

Fig. 4 in Susceptibility of tropical mountain forests to biological invasions from the temperate and subtropical zone, exemplified by Zonitoides (Gastropoda: Gastrodontidae)

Fig. 4. Position of the new locations (L1 and L2, enumeration for each species separately) in Sabah in relation to the Mahalanobis distances of climatic variables for: (a) Zonitoides arboreus s.l., and (b) Z. nitidus. Record ID refers to the order of the data entry.

Fig. 2 in Susceptibility of tropical mountain forests to biological invasions from the temperate and subtropical zone, exemplified by Zonitoides (Gastropoda: Gastrodontidae)

Fig. 2. Global climatic suitability for (a) Zonitoides arboreus s.l. and (b) Zonitoides nitidus based on Mahalanobis distances from the 10 km grid resolution. The higher the threshold, the more dissimilar are the climatic conditions to those of the majority of known occurrences, and>100 % means that the climatic conditions are dissimilar to those of any other available record.

Fig. 1 in Susceptibility of tropical mountain forests to biological invasions from the temperate and subtropical zone, exemplified by Zonitoides (Gastropoda: Gastrodontidae)

Fig. 1. Estimation of the phylogenetic relationships of the COI barcoding sequence from the Zonitoides specimens and two outgroups (labeled with their BOLD or GenBank accession numbers) using the Maximum Likelihood method based on the Tamura-Nei model. The tree with the highest log likelihood (−2138.3583) is shown. Branch lengths equal genetic distances in terms of the number of base substitutions per site. The percentage of replicate trees in which the associated taxa clustered together in the bootstrap test (500 replicates) are shown next to the branches. The tree was constructed in MEGA 6.0. Please note that the shell of (living) Z. nitidus is darkly pigmented, and that the extended animal of the depicted Z. nitidus started fading.

Fig. A2 in Susceptibility of tropical mountain forests to biological invasions from the temperate and subtropical zone, exemplified by Zonitoides (Gastropoda: Gastrodontidae)

Fig. A2. Map of the occurrences of Zonitoides nitidus used for the calculation of climatic suitability for the 10 km grid resolution.