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Fig. 1 in Assemblages of beetles (Coleoptera) in a peatbog and surrounding pine forest

Fig. 1. Comparison of species compositions of beetles registered in different habitats in the Čepkeliai Reserve in 1999 (Sorensen coefficient of similarity, UPGMA linking method).

Figure 4 in Distribution of two pine processionary moth species in Turkey evidences a contact zone

Figure 4. Distribution of pure T. wilkinsoni (black) and T. pityocampa (white), introgressed individuals (gray with Ia and Ib), dispersal routes and barriers, and the contact zone. Color and sign codes are given in the map legend.

Figure 3 in Distribution of two pine processionary moth species in Turkey evidences a contact zone

Figure 3. Consensus haplotype trees for COI, ITS-1, and photolyase. Three clades of wilkinsoni haplotypes are shown in shaded rectangles. All branches have bootstrap support values> 60%.

Figure 1 in Distribution of two pine processionary moth species in Turkey evidences a contact zone

Figure 1. Map of sampling locations and coniferous forests in Turkey and Cyprus (forest data is from EC-JRC Forest Map, 2006).

Figure 2 in Distribution of two pine processionary moth species in Turkey evidences a contact zone

Figure 2. Distribution maps of a) COI, b) ITS-1, and c) photolyase haplotypes. Haplotypes are colored and numbered in accordance with the network. Color and sign codes are given in the legends on the maps. d) Haplotype networks for COI, ITS-1, and photolyase. Numbers on the dashed lines indicate how many mutations separate two relevant haplotypes.

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.

Fig. 7 in Vulnerability of Northern Pine Snakes (Pituophis melanoleucus Daudin, 1803) during fall den ingress in New Jersey, USA

Fig. 7. Schematic of life cycle of Northern Pine Snakes, indicating periods of high vulnerability to human disturbances, such as fire, off-road vehicles, hunting, and poaching.

Fig. 5 in Vulnerability of Northern Pine Snakes (Pituophis melanoleucus Daudin, 1803) during fall den ingress in New Jersey, USA

Fig. 5. Activity of snakes in Fall 2017 and Fall 2018 as a function of the maximum daytime temperature and the previous night's low temperature.

Fig. 3 in Vulnerability of Northern Pine Snakes (Pituophis melanoleucus Daudin, 1803) during fall den ingress in New Jersey, USA

Fig. 3. All activity of snakes at four dens in Bass River State Forest in 2018 as a function of date and soil surface temperature.

Fig. 2 in Vulnerability of Northern Pine Snakes (Pituophis melanoleucus Daudin, 1803) during fall den ingress in New Jersey, USA

Fig. 2. All activity of snakes at den 1 (Bass River State Forest) in 2017 as a function of date and soil surface temperature. The colored markers indicated by 9-digit numbers in the legend represent individually tagged snakes. Data for snakes during the period from 29 October to 11 November (red line) were not recorded because the maximum number of data points the receiver could store was reached.

Fig. 4 in Vulnerability of Northern Pine Snakes (Pituophis melanoleucus Daudin, 1803) during fall den ingress in New Jersey, USA

Fig. 4. Fall activity of snakes in Fall 2017 and Fall 2018 as a function of time of day and surface soil temperature. Activity type is noted by each symbol.

Fig. 6 in Vulnerability of Northern Pine Snakes (Pituophis melanoleucus Daudin, 1803) during fall den ingress in New Jersey, USA

Fig. 6. Activity of two hatchlings (tag numbers 845090639 and 845090603) in the fall of 2018 at den (Davenport) as a function of date and soil surface temperature.

Figure 9. Sometimes many volunteers are necessary for a in Stakeholder contributions to conservation of threatened Northern Pine Snakes (Pituophis melanoleucus, Daudin, 1803) in the New Jersey Pine Barrens as a case study

Figure 9. Sometimes many volunteers are necessary for a project, either digging up a hibernation site (Fig 9a), clearing open areas for sun penetration, or digging up an old septic line to prevent collapses and injuries to snakes.

Fig. 3 in Stakeholder contributions to conservation of threatened Northern Pine Snakes (Pituophis melanoleucus, Daudin, 1803) in the New Jersey Pine Barrens as a case study

Fig. 3. Typical nesting area of Northern Pine Snakes in New Jersey. They require relatively open areas where there is complete sun penetration to the ground to provide sufficient warmth to the incubating eggs (Burger 1989a, 1991a; Burger and Zappalorti 2011a).

Fig. 5 in Stakeholder contributions to conservation of threatened Northern Pine Snakes (Pituophis melanoleucus, Daudin, 1803) in the New Jersey Pine Barrens as a case study

Fig. 5. Pine Snakes hibernate in communal hibernacula that can contain up to 30 or more Pine Snakes (Burger et al. 1988; Burger and Zappalorti 2011a, b, 2015, 2016). Fig. 5a shows the depth hibernation chambers are below ground, a snake in a natural chamber (Fig 5b) and in cement blocks from an old septic chamber (Fig. 5c, Pine Snake on right, Black Racer on left).

Fig. 1 in Stakeholder contributions to conservation of threatened Northern Pine Snakes (Pituophis melanoleucus, Daudin, 1803) in the New Jersey Pine Barrens as a case study

Fig. 1. Northern Pine Snake (Pituophis melanoleucus) hissing when first encountered in the New Jersey Pine Barrens.

Figure 8 in Stakeholder contributions to conservation of threatened Northern Pine Snakes (Pituophis melanoleucus, Daudin, 1803) in the New Jersey Pine Barrens as a case study

Figure 8. Several Pine Snake females often nest in the same nest. Here we (R. Zappalorti and J. Burger) have removed four clutches (note they are bound together, making it possible to identify the eggs of three different females). Once females lay eggs, they exude a liquid that binds the eggs together. This partly prevents other females from disrupting the clutch and accidentally removing them to the outside while they are digging their own side chambers.