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Fig. 6 in SPECIFIC AND TROPHIC DIVERSITY OF SOIL NEMATODES IN FOREST ECOSYSTEMS FROM THE ZARAND MOUNTAINS

Fig. 6. - Relative abundance of the nematode FEeding groups in podzolic brown soil of the dmmast oak FOrest FRom BIIrzava (b).

Fig. 5 in SPECIFIC AND TROPHIC DIVERSITY OF SOIL NEMATODES IN FOREST ECOSYSTEMS FROM THE ZARAND MOUNTAINS

Fig. 5. - Relative abundance of the nematode feeding groups in brown earth soil of the durmast oak forest from Corbe�ti.

Fig. 4 in SPECIFIC AND TROPHIC DIVERSITY OF SOIL NEMATODES IN FOREST ECOSYSTEMS FROM THE ZARAND MOUNTAINS

Fig. 4. - Relative abundance of the nematode feeding groups in brown earth soil of the hoRNbeam-beech FOrest from Cladova (b).

Fig. 2 in SPECIFIC AND TROPHIC DIVERSITY OF SOIL NEMATODES IN FOREST ECOSYSTEMS FROM THE ZARAND MOUNTAINS

Fig. 2. - Relative abundance of the nematode FEeding groups in brown acid soil of the beech forest fRom Miidrige�ti a.

Fig. 3 in SPECIFIC AND TROPHIC DIVERSITY OF SOIL NEMATODES IN FOREST ECOSYSTEMS FROM THE ZARAND MOUNTAINS

Fig. 3. - Relative abundance of the nematode feeding groups in brown acid soil of the hornbeambeech forest from Miidrige�ti (b).

Fig. 1 in SPECIFIC AND TROPHIC DIVERSITY OF SOIL NEMATODES IN FOREST ECOSYSTEMS FROM THE ZARAND MOUNTAINS

Fig. 1. - Dendrogram of cluster analysis FOR nematode communities, based on specific affinity, in the deciduous FOrests from the ZaRand Mountains.

Figure 5 in Impact of rainforest conversion into monoculture plantation systems on pseudoscorpion density, diversity and trophic niches

Figure 5. Stable isotope values of pseudoscorpion species in different land-use systems; means with standard deviation. Dashed horizontal lines represent estimated trophic level boundaries; trophic level 1 (plant material) not shown. Decomposers feeding on detritus (trophic level 2) were assumed to be enriched in 15N by 1.7 ‰ compared to leaf litter, each following trophic level was assumed to span 3.4 ‰ (Post 2002; Potapov et al. 2019a). For abbreviations see Table 1.

Figure 3 in Impact of rainforest conversion into monoculture plantation systems on pseudoscorpion density, diversity and trophic niches

Figure 3. Bootstrap species accumulation curve based on the number of adult individuals in the studied land-use systems.

Figure 4 in Impact of rainforest conversion into monoculture plantation systems on pseudoscorpion density, diversity and trophic niches

Figure 4. Venn diagram of the species composition in the three land-use systems studied (rainforest, rubber, oil palm) in the Bukit Duabelas (left) and Harapan landscape (right). Landscape-specific species are underlined in red. The riparian-specific species in Harapan is underlined in cyan. For abbreviations see Table 1.

Figure 2 in Impact of rainforest conversion into monoculture plantation systems on pseudoscorpion density, diversity and trophic niches

Figure 2. Density of pseudoscorpions in litter and soil of the three land-use systems studied (rainforest, rubber, oil palm) in the Bukit Duabelas and Harapan landscape. Each data point represents one sampling plot (three pooled subplot samples). Only non-riparian sites are shown.

Figure 1 in Impact of rainforest conversion into monoculture plantation systems on pseudoscorpion density, diversity and trophic niches

Figure 1. Four species of pseudoscorpions found at the study sites. From left to right: Atemnidae sp.1, Lagynochthonius sp.1, Atemnidae sp.2, Hya minuta.

Fig. 3 in Effects of latitude, host body size, and host trophic guild on patterns of diversity of helminths associated with humans, wild and domestic mammals of Mexico

Fig. 3. Phylogenetic generalized least squares (PGLS) regression of host body mass (values were log-transformed) with richness of helminths associated to wildlife hosts (values were corrected for sampling effort).

Fig. 2 in Effects of latitude, host body size, and host trophic guild on patterns of diversity of helminths associated with humans, wild and domestic mammals of Mexico

Fig. 2. Relationships between latitude and the average taxonomic distinctness of overall helminths (A) and nematodes (B).

Fig. 4 in Effects of latitude, host body size, and host trophic guild on patterns of diversity of helminths associated with humans, wild and domestic mammals of Mexico

Fig. 4. Parasite richness and average taxonomic distinctness by host trophic guild (the size of circle represents the number of hosts belonging to each trophic guild).

Fig. 1 in Effects of latitude, host body size, and host trophic guild on patterns of diversity of helminths associated with humans, wild and domestic mammals of Mexico

Fig. 1. Maps showing the geographic locations of the records, classified by phylum of the subsetted database.