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Figure 3 in Population dynamics and reproduction of the hermit crab Calcinus gaimardii (Anomura: Diogenidae) at Inhaca Island, southern Mozambique

Figure 3. Calcinus gaimardii (H. Milne Edwards, 1848). Relationship between sex ratio and crab size.

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Figure 2 in Population dynamics and reproduction of the hermit crab Calcinus gaimardii (Anomura: Diogenidae) at Inhaca Island, southern Mozambique

Figure 2. Calcinus gaimardii (H. Milne Edwards, 1848). Frequency of crabs sampled at Inhaca Island during the study period.

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Figure 1 in Population dynamics and reproduction of the hermit crab Calcinus gaimardii (Anomura: Diogenidae) at Inhaca Island, southern Mozambique

Figure 1. Whisker plots (mean¡SD) representing size variation of Calcinus gaimardii (H. Milne Edwards, 1848) of males (A) and females (B).

Fig. 1 in Population Dynamics Of Arboreal And Terrestrial Small Mammals In A Tropical Rainforest, Sarawak, Malaysia

Fig. 1. Temporal patterns at Lambir Hills National Park, Sarawak, Malaysia, from August 1997 to December 2005. (a) percentage of fruiting trees obtained by phenology observation (%; black circle), together with weight of dried fruits obtained by seed traps from November 2000 to December 2005 (g/m2; white circle); (b) population dynamics per 100 trapnights of arboreal and terrestrial small mammals; (c) percentage of the two age classes (immature and adult) of Maxomys rajah. Total numbers of captured M. rajah at each census were shown.

Fig. 1 in A Preliminary Study Of Two Sympatric Maxomys Rats In Sarawak, Malaysia: Spacing Patterns And Population Dynamics

Fig. 1: a) Location of the study area, Lambir Hills National Park, Sarawak, Malaysia (black circle); b) Distribution of wire-mesh live cage traps (black circles) set at the Canopy Biology Plot.

Fig. 2 in A Preliminary Study Of Two Sympatric Maxomys Rats In Sarawak, Malaysia: Spacing Patterns And Population Dynamics

Fig. 2. Distribution of the home ranges of Maxomys rajah and M. whiteheadi during: a) August 1997–July 1999; b) May 2001–July 2004; and c) November 2004–July 2005. M, male; F, female.

Fig. 3 in A Preliminary Study Of Two Sympatric Maxomys Rats In Sarawak, Malaysia: Spacing Patterns And Population Dynamics

Fig. 3. Population dynamics of Maxomys rajah (open circles) and M. whiteheadi (black squares) from August 1997 to July 2005 at Lambir hills National Park, Sarawak, Malaysia.

Fig. 1 in Population dynamics of corallivores (Drupella and Acanthaster) on coral reefs of Koh Tao, a diving destination in the Gulf of Thailand

Fig. 1. Map of survey sites used in this study (after Hoeksema et al., 2012). Six of them were monitored for hard coral cover: Hin Wong Bay, Sairee, Sai Nuan, Chalok Ban Kao, Ao Leuk, and Tanote Bay. These sites and two additional ones (Mango Bay and Twin Rocks=Twins) were also used for predator studies.

Fig. 3 in Population dynamics of corallivores (Drupella and Acanthaster) on coral reefs of Koh Tao, a diving destination in the Gulf of Thailand

Fig. 3. Population dynamics of coral predators around Koh Tao in 2006–2014. a, Relative Drupella abundance showing significant variation over time (p=0.013). b, Mean Acanthaster abundance not varying significantly over time (p=0.189). c, Mean Drupella abundance is significantly higher in shallow quadrats as compared to deeper ones (p <0.001). d, Mean Acanthaster abundance shows no difference by depth (p=0.142). e, Mean Drupella abundance by site varied significantly (p <0.001). f, Mean Acanthaster abundance by site varied significantly p <0.001). g, Seasonal variability in Acanthaster abundance at EMP sites was not significant (p=0.641).

Fig. 5 in Population dynamics of corallivores (Drupella and Acanthaster) on coral reefs of Koh Tao, a diving destination in the Gulf of Thailand

Fig. 5. Coral predator abundance compared to previously published results on Koh Tao's reefs; differences are not significant. Drupella (a) and Acanthaster (b) abundance in low- and high-use sites as designated by Lamb et al. (2014). Similar for the designations as MPA or non-MPA sites used by Hein et al. (2014) concerning Drupella (c) and Acanthaster (d).

Fig. 4 in Population dynamics of corallivores (Drupella and Acanthaster) on coral reefs of Koh Tao, a diving destination in the Gulf of Thailand

Fig. 4. Positive linear correlation between Drupella abundance and live hard coral cover (R2=0.572, p <0.001).

Fig. 2 in Population dynamics of corallivores (Drupella and Acanthaster) on coral reefs of Koh Tao, a diving destination in the Gulf of Thailand

Fig. 2. Variation in mean hard coral cover at Koh Tao over the period 2006–2014 for the six selected sites indicated in Table 1.

Fig. 6 in Spatiotemporal dynamics of insect diversity in tropical seasonal forests is linked to season and elevation, a case from northern Thailand

Fig. 6. Variation in Equitability (J) and Berger-Parker dominance (DBP) of Diptera (A) and Auchenorrhyncha (B) during 12 months of sampling over six 500 m elevation zones at Doi Inthanon in 2014. Values of J (bars) and DBP (lines) were computed in PAST and 95% confidence intervals obtained by bootstrapping using 9999 random samples. In Kruskal-Wallis H-tests there was a significant difference between the medians for Berger-Parker dominance in Diptera (H = 26.7, p <0.01) and Auchenorrhyncha (H = 14.9, p <0.01). Equitability was significantly different for Diptera (H = 36.5, p <0.01) but not for Auchenorrhyncha (H = 10.7, p = 0.0582).

Fig. 10 in Spatiotemporal dynamics of insect diversity in tropical seasonal forests is linked to season and elevation, a case from northern Thailand

Fig. 10. Variation in Mean Monthly Turnover (βwM) of Diptera (A) and Auchenorrhyncha (B) during 12 months of sampling over six 500 m elevation zones at Doi Inthanon in 2014. The mean value of βwM in each elevation zone ± standard error is indicated. Note that the vertical axis does not extend to zero. In Kruskal-Wallis H-tests there was a significant difference between the medians for Diptera (H = 29.0, p <0.01) and Auchenorrhyncha (H = 22.1, p <0.01).

Fig. 2 in Spatiotemporal dynamics of insect diversity in tropical seasonal forests is linked to season and elevation, a case from northern Thailand

Fig. 2. Observed species richness (Sobs) of Diptera and Auchenorrhyncha trapped in six elevation zones over 12 months sampling at Doi Inthanon in 2014. Diptera, open circles; Auchenorrhyncha, closed circles.). In Kruskal-Wallis H-tests there was a significant difference between the medians for Diptera (H = 22.1, p <0.01) and Auchenorrhyncha (H = 14.3, p <0.05).

Fig. 1. Relative abundance, A in Spatiotemporal dynamics of insect diversity in tropical seasonal forests is linked to season and elevation, a case from northern Thailand

Fig. 1. Relative abundance, A* (number of individuals caught. trap-1. month-1) of Diptera and Auchenorrhyncha trapped in six elevation zones over 12 months sampling at Doi Inthanon in 2014. Standard errors indicated. Note log10 scale. Data were fitted to a linear regression model in PAST; Diptera, open circles (r2 = 0.8567, p = 0.0081); Auchenorrhyncha, closed circles (r2 = 0.3182, p = 0.2434). In Kruskal-Wallis H-tests of untransformed data there was a significant difference between the medians for Diptera (H = 29.3, p <0.01) but not for Auchenorrhyncha (H = 3.3, p = 0.657).

Fig. 8 in Spatiotemporal dynamics of insect diversity in tropical seasonal forests is linked to season and elevation, a case from northern Thailand

Fig. 8. Variation in species turnover measured as βw of Diptera (a) and Auchenorrhyncha (b) during 12 months of sampling over six 500 m elevation zones at Doi Inthanon in 2014. Pairwise calculations of βw between each quadrat of a grid of elevation and month with the quadrat with maximum species richness (April/1,500–2,000 m quadrat for Diptera and June/500–1,000 m quadrat for Auchenorrhyncha) were mapped using the multiquadric gridding algorithm in the gridding module of PAST. Values of βw (indicated by colour scale bar) vary between 0 (complete identity) and 1.0 (complete non-identity). Data are not available for January and February at <500 m and 500–1,000 m.

Fig. 3. Relative abundance, A in Spatiotemporal dynamics of insect diversity in tropical seasonal forests is linked to season and elevation, a case from northern Thailand

Fig. 3. Relative abundance, A* (number of individuals caught. trap-1. month-1) of Diptera and Auchenorrhyncha over 12 months sampling at Doi Inthanon in 2014. Standard errors indicated. Note log10 scale. In Kruskal-Wallis H-tests of untransformed data there was a significant difference between the medians for Diptera (H = 24.5, p <0.05) and Auchenorrhyncha (H = 34.3, p <0.01).

Fig. 9 in Spatiotemporal dynamics of insect diversity in tropical seasonal forests is linked to season and elevation, a case from northern Thailand

Fig. 9. Spatiotemporal variation in species turnover measured as Mean Local Turnover βwL of Diptera (A) and Auchenorrhyncha (B) trapped during 12 months of sampling over six 500 m elevation zones at Doi Inthanon in 2014. Data were plotted on a grid of elevation zone (vertical axis) and months (horizontal axis) and mapped using the multiquadric gridding algorithm in the gridding module of PAST. Values of βwL (indicated by colour scale bar) vary between 0 (complete identity) and 1.0 (complete non-identity). Data are not available for January and February at <500 m and 500–1,000 m.

Fig. 7 in Spatiotemporal dynamics of insect diversity in tropical seasonal forests is linked to season and elevation, a case from northern Thailand

Fig. 7. Monthly variation in Equitability (J) of Diptera assemblages during 12 months of sampling over six 500 m elevation zones at Doi Inthanon in 2014. Only points linking data from elevation zones 2,000–2,500 m and>2,500 m are connected by lines. Equitability declines profoundly at higher elevations between September and November indicating a decline in evenness of Diptera assemblages with corresponding prevalence of a number of relatively abundant species compared with other times of year and other elevations.