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430 results for “meadow”
Figure 5 from: Kenyeres Z, Szentirmai I (2017) Effects of different mowing regimes on orthopterans of Central-European mesic hay meadows. Journal of Orthoptera Research 26: 29-37. https://doi.org/10.3897/jor.26.14549
Figure 5 - Box-plots (median values with minimum, maximum and ±SE) of nymphal density (specimen/m2) of orthopterans in four treatment types (mowing once a year in May; mowing twice a year in May and September; mowing once a year in September; abandoned) in June (Jn), July (Jl) and August (Ag). Significant (p<0.05) differences detected by Mann-Whitney U test are indicated by different letters.
Figure 4 from: Kenyeres Z, Szentirmai I (2017) Effects of different mowing regimes on orthopterans of Central-European mesic hay meadows. Journal of Orthoptera Research 26: 29-37. https://doi.org/10.3897/jor.26.14549
Figure 4 - Box-plots (median values with minimum, maximum and ±SE) of species richness, adult density (specimen/m2) and Shannon diversity of orthopterans in four treatment types (mowing once a year in May; mowing twice a year in May and September; mowing once a year in September; abandoned) in June (Jn), July (Jl) and August (Ag). Significant (p<0.05) differences detected by Mann-Whitney U test are indicated by different letters.
Figure 3 from: Kenyeres Z, Szentirmai I (2017) Effects of different mowing regimes on orthopterans of Central-European mesic hay meadows. Journal of Orthoptera Research 26: 29-37. https://doi.org/10.3897/jor.26.14549
Figure 3 - Box-plots (median values with minimum, maximum and ±SE) of species richness, density (specimen/m2) and Shannon diversity of orthopterans in four treatment types of sites I–IV. Significant (p<0.05) differences detected by Mann-Whitney U test are indicated by different letters.
Figure 1 from: Kenyeres Z, Szentirmai I (2017) Effects of different mowing regimes on orthopterans of Central-European mesic hay meadows. Journal of Orthoptera Research 26: 29-37. https://doi.org/10.3897/jor.26.14549
Figure 1 - Location of the four study sites in Őrség National Park and the quadrats of different mowing regimes (quadrats are 20 × 20 metres; M: mowing once a year in May; MS: mowing twice a year in May and September; S: mowing once a year in September; C: abandoned).
Figure 2 from: Kenyeres Z, Szentirmai I (2017) Effects of different mowing regimes on orthopterans of Central-European mesic hay meadows. Journal of Orthoptera Research 26: 29-37. https://doi.org/10.3897/jor.26.14549
Figure 2 - Box-plots (median values with minimum, maximum and ±SE) of vegetation height in four treatment types. Significant (p<0.05) differences detected by Mann-Whitney U test are indicated by different letters.
Figure 6 from: Kenyeres Z, Szentirmai I (2017) Effects of different mowing regimes on orthopterans of Central-European mesic hay meadows. Journal of Orthoptera Research 26: 29-37. https://doi.org/10.3897/jor.26.14549
Figure 6 - PCA based on the orthopteran samples of four study sites (sites I–IV) (black circle: mowing once a year in May; black square: mowing twice a year in May and September; empty circle: mowing once a year in September; black triangle: abandoned).
Figure 5 from: Kenyeres Z, Szentirmai I (2017) Effects of different mowing regimes on orthopterans of Central-European mesic hay meadows. Journal of Orthoptera Research 26: 29-37. https://doi.org/10.3897/jor.26.14549
Figure 5 - Box-plots (median values with minimum, maximum and ±SE) of nymphal density (specimen/m2) of orthopterans in four treatment types (mowing once a year in May; mowing twice a year in May and September; mowing once a year in September; abandoned) in June (Jn), July (Jl) and August (Ag). Significant (p<0.05) differences detected by Mann-Whitney U test are indicated by different letters.
Figure 2 from: Kenyeres Z, Szentirmai I (2017) Effects of different mowing regimes on orthopterans of Central-European mesic hay meadows. Journal of Orthoptera Research 26: 29-37. https://doi.org/10.3897/jor.26.14549
Figure 2 - Box-plots (median values with minimum, maximum and ±SE) of vegetation height in four treatment types. Significant (p<0.05) differences detected by Mann-Whitney U test are indicated by different letters.
Figure 3 from: Kenyeres Z, Szentirmai I (2017) Effects of different mowing regimes on orthopterans of Central-European mesic hay meadows. Journal of Orthoptera Research 26: 29-37. https://doi.org/10.3897/jor.26.14549
Figure 3 - Box-plots (median values with minimum, maximum and ±SE) of species richness, density (specimen/m2) and Shannon diversity of orthopterans in four treatment types of sites I–IV. Significant (p<0.05) differences detected by Mann-Whitney U test are indicated by different letters.
Figure 1 from: Kenyeres Z, Szentirmai I (2017) Effects of different mowing regimes on orthopterans of Central-European mesic hay meadows. Journal of Orthoptera Research 26: 29-37. https://doi.org/10.3897/jor.26.14549
Figure 1 - Location of the four study sites in Őrség National Park and the quadrats of different mowing regimes (quadrats are 20 × 20 metres; M: mowing once a year in May; MS: mowing twice a year in May and September; S: mowing once a year in September; C: abandoned).
Figure 4 from: Kenyeres Z, Szentirmai I (2017) Effects of different mowing regimes on orthopterans of Central-European mesic hay meadows. Journal of Orthoptera Research 26: 29-37. https://doi.org/10.3897/jor.26.14549
Figure 4 - Box-plots (median values with minimum, maximum and ±SE) of species richness, adult density (specimen/m2) and Shannon diversity of orthopterans in four treatment types (mowing once a year in May; mowing twice a year in May and September; mowing once a year in September; abandoned) in June (Jn), July (Jl) and August (Ag). Significant (p<0.05) differences detected by Mann-Whitney U test are indicated by different letters.
Figures 5-8 from: Caleb JTD, Sajan SK, Kumar V (2018) New jumping spiders from the alpine meadows of the Valley of Flowers, western Himalayas, India (Araneae, Salticidae). ZooKeys 783: 113-124. https://doi.org/10.3897/zookeys.783.25225
Figures 5-8 Nandiciusvallisflorum sp. n., holotype female. 5 epigyne, ventral view 6 vulva, dorsal view 7 epigyne, ventral view 8 vulva, dorsal view. Abbreviations: Co – copulatory opening; Cd – copulatory duct; Ep – epigynal pocket; Fd – fertilization duct; S – spermatheca. Scale bars: 0.1 mm.
Figures 14-19 from: Caleb JTD, Sajan SK, Kumar V (2018) New jumping spiders from the alpine meadows of the Valley of Flowers, western Himalayas, India (Araneae, Salticidae). ZooKeys 783: 113-124. https://doi.org/10.3897/zookeys.783.25225
Figures 14-19 Pelleneshimalaya sp. n., 14–17 paratype female (AA1644). 14 general appearance, dorsal view 15 same, lateral view 16 chelicerae, ventral view 17 front view 18 front view of paratype (AA1638) 19 epigyne, ventral view of paratype (AA1638). Scale bars: 1 mm (14–15); 0.5 mm (17–18); 0.2 mm (19).
Figures 20-24 from: Caleb JTD, Sajan SK, Kumar V (2018) New jumping spiders from the alpine meadows of the Valley of Flowers, western Himalayas, India (Araneae, Salticidae). ZooKeys 783: 113-124. https://doi.org/10.3897/zookeys.783.25225
Figures 20-24 Pelleneshimalaya sp. n., holotype male. 20 male left palp, ventral view 21 same, ventro-lateral view 22, same, retrolateral view 23 same, dorso-lateral view 24 same, dorsal view. Scale bars: 0.2 mm (20–24). Abbreviations: CL – cymbial lobe; RTA – retrolateral tibial apophysis; Sd – sperm duct.
Figures 25-27 from: Caleb JTD, Sajan SK, Kumar V (2018) New jumping spiders from the alpine meadows of the Valley of Flowers, western Himalayas, India (Araneae, Salticidae). ZooKeys 783: 113-124. https://doi.org/10.3897/zookeys.783.25225
Figures 25-27 Pelleneshimalaya sp. n., holotype male. 25 male left palp, ventral view 26 same, ventro-lateral view 27 left leg I, prolateral view. Scale bars: 0.1 mm (25–27). Abbreviations: CTA – compound terminal apophysis; E – embolus; RTA – retrolateral tibial apophysis; Sd – sperm duct.
Figures 1-4 from: Caleb JTD, Sajan SK, Kumar V (2018) New jumping spiders from the alpine meadows of the Valley of Flowers, western Himalayas, India (Araneae, Salticidae). ZooKeys 783: 113-124. https://doi.org/10.3897/zookeys.783.25225
Figures 1-4 Nandiciusvallisflorum sp. n., holotype female. 1 general appearance, dorsal view 2 same, ventral view 3 same, lateral view 4 front view. Scale bars: 1 mm (1–3), 0.5 mm (4).
Figure 31 from: Caleb JTD, Sajan SK, Kumar V (2018) New jumping spiders from the alpine meadows of the Valley of Flowers, western Himalayas, India (Araneae, Salticidae). ZooKeys 783: 113-124. https://doi.org/10.3897/zookeys.783.25225
Figure 31 Alpine meadow habitat of Nandiciusvallisflorum sp. n. and Pelleneshimalaya sp. n. Image was kindly provided by Dibyajyoti Ghosh.
Figures 28-30 from: Caleb JTD, Sajan SK, Kumar V (2018) New jumping spiders from the alpine meadows of the Valley of Flowers, western Himalayas, India (Araneae, Salticidae). ZooKeys 783: 113-124. https://doi.org/10.3897/zookeys.783.25225
Figures 28-30 Pelleneshimalaya sp. n., paratype (AA1644). 28 epigyne, ventral view 29 vulva, dorsal view 30 same. Abbreviations: CBP – central blind pocket; Cd – copulatory duct; Fd – fertilization duct; S – spermatheca. Scale bars: 0.1 mm (28–30).
Figures 9-13 from: Caleb JTD, Sajan SK, Kumar V (2018) New jumping spiders from the alpine meadows of the Valley of Flowers, western Himalayas, India (Araneae, Salticidae). ZooKeys 783: 113-124. https://doi.org/10.3897/zookeys.783.25225
Figures 9-13 Pelleneshimalaya sp. n. 9–11 general appearance. 9 dorsal view (holotype) 10 ventral view 11 dorsal view of paratype (AA1646). 12–13 carapace, front views. 12 holotype 13 paratype (AA1645). Scale bars: 1 mm (9–11); 0.5 mm (12–13).
Dataset on: Records of sea star (Echinodermata, Asteroidea) diversity in a disturbed tropical seagrass meadow
<p>This study aims to record the sea star distribution in seagrass meadows within Sungai Pulai estuary (Johor, Malaysia) that is under pressure from coastal modification activities. The sampling sites were Merambong Shoal, Tanjung Adang Shoal, Tanjung Bin and Sungai Duku. From January 2016 to March 2018, we surveyed the areas to provide an inventory of sea star species sighted during the lowest tides. A total of seven species were observed, with Merambong Shoal having the highest number of species (seven species) while Sungai Duku and Tanjung Bin had the lowest (one species). We report the first sighting of <em>Astropecten vappa</em> in the area. Combined with past studies, there are now a total of eight sea star species in this area. As baseline records, our findings for the sea star community are applicable to the management of the seagrass habitat and help to create awareness of sea star diversity in the area.</p>
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