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146 results for “Wet Tropics”

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zenodo32/100

FIGURE 1 in Caridina malanda, a new species of freshwater shrimp (Crustacea: Decapoda Atyidae) from the Wet Tropics World Heritage area, north-eastern Queensland Australia

FIGURE 1. Literature records of Caridina from the C. zebra complex from the Wet Tropics of north–eastern Queensland, Australia. Light green shading indicates national parks, forest reserves, and protected areas (Collaborative Australian Protected Areas database [CAPAD], 2010, https://data.gov.au/data/dataset/1f420717-e600-4ff0-8c04-90122bfa04a7, accessed 2019, May 7).

opennotspecifiedAug 2019View details →
zenodo32/100

FIGURE 3 in Caridina malanda, a new species of freshwater shrimp (Crustacea: Decapoda Atyidae) from the Wet Tropics World Heritage area, north-eastern Queensland Australia

FIGURE 3. Caridina malanda sp. nov. (A) anterior region of cephalothorax; (B) first pereiopod; (C) second pereiopod; (D) third pereiopod; (E) dactylus of third pereiopod; (F) fifth pereiopod; (G) dactylus of fifth pereiopod; (H) first male pleopod; (I) second male pleopod; (J) posterior margin of telson. Scale bars: in mm. Drawings based on A: holotype, female, site 24, Malanda Creek, deposited QM (Queensland Museum), registration number W29455. B and C: female, site 23, Short Creek, deposited QM W29457. D and E: large male, site 30, Ithaca River, deposited AM (Australian Museum), registration number P.103599. Note: the dactylus of the third pereiopod is not sexually dimorphic. F: female, site 24, Malanda Creek, deposited AM P.103594. G: male, site 23, Short Creek, QM W29456. H and I: male, site 22, Brodie Creek, deposited AM P.103600. J: female specimen from site 32, Johnstone River, deposited AM P.103596.

opennotspecifiedAug 2019View details →
zenodo32/100

FIGURE 2 in Caridina malanda, a new species of freshwater shrimp (Crustacea: Decapoda Atyidae) from the Wet Tropics World Heritage area, north-eastern Queensland Australia

FIGURE 2. Caridina malanda sp. nov. (A) Paratype, preserved in ethanol, Site 23, Short Creek, deposited in QM (Queensland Museum, Australia), registration number W29457; (B) Ovigerous female, preserved in ethanol, Site 32, Johnstone River, deposited QM W29458; (C, D) Colouration on capture, Site 24, Malanda Creek; (E) Live colouration in aquaria, Site 20, Barney Springs; (F) Caridina zebra Short 1993; (G) Caridina confusa Choy & Marshall 1997; (H) Top. C. confusa, preserved in ethanol. Bottom. C. malanda sp. nov. preserved in ethanol; both specimens collected at Site 23, Short Creek. Photos A, B, H by S. Choy; C–G by B. Mos.

opennotspecifiedAug 2019View details →
zenodo32/100

FIGURE. 5 in Caridina malanda, a new species of freshwater shrimp (Crustacea: Decapoda Atyidae) from the Wet Tropics World Heritage area, north-eastern Queensland Australia

FIGURE. 5. Caridina malanda sp. nov. (A) first pereiopod; (B) second pereiopod; (C) dactylus of third pereiopod; (D) dactylus of fifth pereiopod; (E) Left. antennal flagellum. Right. antennule with stylocerite; (F) Left. first male pleopod. Right. second male pleopod; (G) posterior margin of telson; (H) lateral view of posterior of abdomen, showing telson, uropods and fifth pleopod. Photos: A, B, E are female specimen from site 23, Short Creek, deposited QM (Queensland Museum), registration number W29457; C is large male specimen from site 30, Ithaca River, deposited AM (Australian Museum), registration number P.103599. D is male specimen from site 23, Short Creek, deposited QM W29456. F is male specimen from site 22, Brodie Creek, deposited AM P.103600. G is female specimen from site 32, Johnstone River, deposited AM P.103596; H is holotype, female specimen, site 24, Malanda Creek, deposited QM W29455. Photos by S. Choy and B. Mos.

opennotspecifiedAug 2019View details →
zenodo32/100

TABLE 1 in Caridina malanda, a new species of freshwater shrimp (Crustacea: Decapoda Atyidae) from the Wet Tropics World Heritage area, north-eastern Queensland Australia

<p><b>TABLE 1.</b> Specimen information of <i>Caridina</i> included in molecular analyses, with relevant GenBank accession numbers. All sequences are new to this paper unless otherwise specified; * = de Mazancourt <i>et al.</i> (2019), # = Page <i>et al.</i> (2007). Reg. No. = registration number for specimen deposited with the Mus&eacute;um national d&rsquo;Histoire naturelle, Paris, France.</p><table><tbody><tr><th><b>Species</b></th><th><b>Site (Catchment)</b></th><th><b>Reg. No.</b></th><th><b>Spec. No.</b></th><th><b>COI</b></th><th><b>16S</b></th></tr></tbody><tbody><tr><th><i>C. malanda</i></th><td>Site 30, Ithaca River</td><td>MNHN-IU-2014-</td><td>CA1735</td><td>MK883793</td><td>MK880178</td></tr><tr><th></th><td>(Johnstone)</td><td>20766</td><td></td><td></td><td></td></tr><tr><th><i>C. malanda</i></th><td>Site 30, Ithaca River</td><td>MNHN-IU-2014-</td><td>CA1736</td><td>MK190071 *</td><td>MK189911 *</td></tr><tr><th></th><td>(Johnstone)</td><td>20767</td><td></td><td></td><td></td></tr><tr><th><i>C. malanda</i></th><td>Site 23, Short Creek</td><td>MNHN-IU-2014-</td><td>CA1737</td><td>MK190072 *</td><td>MK189912 *</td></tr><tr><th></th><td>(Johnstone)</td><td>20768</td><td></td><td></td><td></td></tr><tr><th><i>C. malanda</i></th><td>Site 23, Short Creek</td><td>MNHN-IU-2014-</td><td>CA1738</td><td>MK883796</td><td>MK880181</td></tr><tr><th></th><td>(Johnstone)</td><td>20769</td><td></td><td></td><td></td></tr><tr><th><i>C. malanda</i></th><td>Site 22, Brodie Creek</td><td>MNHN-IU-2014-</td><td>CA1739</td><td>MK883797</td><td>MK880182</td></tr><tr><th></th><td>(Johnstone)</td><td>20770</td><td></td><td></td><td></td></tr><tr><th><i>C. malanda</i></th><td>Site 22, Brodie Creek</td><td>MNHN-IU-2014-</td><td>CA1740</td><td>MK883798</td><td>MK880183</td></tr><tr><th></th><td>(Johnstone)</td><td>20771</td><td></td><td></td><td></td></tr><tr><th><i>C. malanda</i></th><td>Site 24, Malanda Creek</td><td>MNHN-IU-2014-</td><td>CA1741</td><td>MK883799</td><td>MK880184</td></tr><tr><th></th><td>(Johnstone)</td><td>20772</td><td></td><td></td><td></td></tr><tr><th><i>C. malanda</i></th><td>Site 24, Malanda Creek</td><td>MNHN-IU-2014-</td><td>CA1742</td><td>MK883800</td><td>MK880185</td></tr><tr><th></th><td>(Johnstone)</td><td>20773</td><td></td><td></td><td></td></tr><tr><th><i>C. malanda</i></th><td>Site 20, Barney Springs</td><td>MNHN-IU-2014-</td><td>CA1749</td><td>MK883801</td><td>MK880186</td></tr><tr><th></th><td>(Barron)</td><td>20774</td><td></td><td></td><td></td></tr><tr><th><i>C. malanda</i></th><td>Site 20, Barney Springs</td><td>MNHN-IU-2014-</td><td>CA1750</td><td>Mk883802</td><td>MK880187</td></tr><tr><th></th><td>(Barron)</td><td>20775</td><td></td><td></td><td></td></tr><tr><th><i>C. zebra</i></th><td>Tributary of Tully River</td><td>MNHN-IU-2014-</td><td>CA1731</td><td>MK190069 *</td><td>MK189909 *</td></tr><tr><th></th><td>(Tully)</td><td>20776</td><td></td><td></td><td></td></tr><tr><th><i>C. confusa</i></th><td>Thiara Creek</td><td>MNHN-IU-2014-</td><td>CA1727</td><td>MK190067 *</td><td>MK189907 *</td></tr><tr><th></th><td>(Johnstone)</td><td>20777</td><td></td><td></td><td></td></tr><tr><th><i>C. spinula</i></th><td>McIlwraith Range</td><td>-</td><td>GUCCI1</td><td>-</td><td>DQ478527 #</td></tr><tr><th></th><td>(Lockhart)</td><td></td><td></td><td></td><td></td></tr><tr><th><i>C. typus</i></th><td>New Caledonia</td><td>MNHN-IU-2014-</td><td>CA1568</td><td>MK190052 *</td><td>MK189893 *</td></tr><tr><th></th><td></td><td>20778</td><td></td><td></td><td></td></tr></tbody></table>

opennotspecifiedAug 2019View details →
dryad32/100

Coarse woody debris density and carbon concentration by decay classes in mixed montane wet tropical forests (Dataset)

<p>This dataset contains data from a study considering the relationship between decay class, wood density and C content of CWD in old-growth mixed monsoon montane tropical forests in Vietnam based on the inventory of 359 CWD pieces.</p> <p>The CWD inventories were conducted on forty one (3-4 per site) 50 m long and 4 m wide transects. The first dataset for contains site description, plot and transect numbers with geographical coordinates. All CWD pieces of more than 6 cm in diameter were inventoried. The dataset contains position of CWD: stumps, standing dead trees (snags), lying logs, leaning logs and branches, diameter, proportion consumed by termites, decay class, bulk density and moisture of wood and mass loss. The second dataset contains the data on the wood density of tree species present in the study area according to the global database compiled by Zanne et al. (2009).</p>

opencc-zeroSep 2021View details →
dryad32/100

Timing is everything: Acoustic niche partitioning in two tropical wet forest bird communities

<p><span><span><span><span><span><span><span><span><span><span><span>When acoustic signals sent from individuals overlap in frequency and time, acoustic interference and signal masking may occur. Under the acoustic niche hypothesis (ANH), signaling behavior has evolved to partition acoustic space and minimize overlap with other calling individuals through selection on signal structure and/or the sender's ability to adjust the timing of signals. Alternately, under the acoustic clustering hypothesis, there is potential benefit to convergence and synchronization of the structural or temporal characteristics of signals in the avian community, and organisms produce signals that overlap more than would be expected by chance. Interactive communication networks may also occur, where species living together are more likely to have songs with convergent spectral and or temporal characteristics. In this study, we examine the fine-scale use of acoustic space in montane tropical wet forest bird communities in Costa Rica and Hawai'i. At multiple recording stations in each community, we identified the species associated with each recorded signal, measured observed signal overlap, and used null models to generate random distributions of expected signal overlap. We then compared observed vs. expected signal overlap to test predictions of the acoustic niche and acoustic clustering hypotheses. We found a high degree of overlap in the signal characteristics (frequency range) of species in both Costa Rica and Hawai'i, however, as predicted under ANH, species significantly reduced observed overlap relative to the random distribution through temporal partitioning. There was little support for acoustic clustering or the prediction of the network hypothesis that species segregate across the landscape based on the frequency range of their vocalizations. These findings constitute strong support that there is competition for acoustic space in these signaling communities, and this has resulted primarily in temporal partitioning of the soundscape.</span></span></span></span></span></span></span></span></span></span></span></p>

opencc-zeroOct 2021View details →
zenodo32/100

FIGURE 2 in New records of riverweeds (Podostemaceae) from the tropical Andes (Ecuador and Colombia): getting our feet wet to bypass collection bias in Neotropical rivers

FIGURE 2. Map of tropical South America with past records (blue) and the records published in this study (black) of Lophogyne aeruginosa (triangles) and Tristicha trifaria (cross marks).

opennotspecifiedMar 2023View details →
dryad32/100

Coarse woody debris density and carbon concentration by decay classes in mixed montane wet tropical forests (Dataset)

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publicSep 2021View details →
dryad32/100

Data from: Short-term precipitation exclusion alters microbial responses to soil moisture in a wet tropical forest

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publicJul 2018View details →
dryad32/100

Tree species of wet tropical forests differ in their tissue biochemistry and effects on soil carbon dynamics

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publicApr 2021View details →
dryad32/100

Data from: Primary productivity is related to niche width in the Australian Wet Tropics

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publicAug 2019View details →
dryad32/100

Data from: Ants as ecological indicators of rainforest restoration: community convergence and the development of an Ant Forest Indicator Index in the Australian wet tropics

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publicApr 2018View details →
dryad32/100

Timing is everything: Acoustic niche partitioning in two tropical wet forest bird communities

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publicOct 2021View details →
dryad32/100

Tree functional traits as predictors of microburst-associated treefalls in tropical wet forests

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publicJan 2020View details →
dryad32/100

Data from: Mean annual temperature influences local fine root proliferation in tropical montane wet forest

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publicApr 2021View details →
dryad32/100

Data from: Effects of dispersal‐ and niche‐based factors on tree recruitment in tropical wet forest restoration

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publicMar 2020View details →
zenodo28/100

Supplementary material 1 from: Tan MK, Yeo H, Hwang WS (2017) Ground dwelling pygmy grasshoppers (Orthoptera: Tetrigidae) in Southeast Asian tropical freshwater swamp forest prefer wet microhabitats. Journal of Orthoptera Research 26: 73-80. https://doi.org/10.3897/jor.26.14551

: Data type: Table

opencc-by-4.0Jun 2017View details →
zenodo28/100

Figure 4 from: Tan MK, Yeo H, Hwang WS (2017) Ground dwelling pygmy grasshoppers (Orthoptera: Tetrigidae) in Southeast Asian tropical freshwater swamp forest prefer wet microhabitats. Journal of Orthoptera Research 26: 73-80. https://doi.org/10.3897/jor.26.14551

Figure 4 - A canonical analysis of principal coordinates (CAP) with Euclidean distance to show association of adult assemblage with NMDS1 and NMDS2 representing microhabitat conditions. The circle represents belt transects and cross represents morpho-species.

opencc-by-4.0Jun 2017View details →
zenodo28/100

Figure 3 from: Tan MK, Yeo H, Hwang WS (2017) Ground dwelling pygmy grasshoppers (Orthoptera: Tetrigidae) in Southeast Asian tropical freshwater swamp forest prefer wet microhabitats. Journal of Orthoptera Research 26: 73-80. https://doi.org/10.3897/jor.26.14551

Figure 3 - Correlation between total abundance of pygmy grasshoppers and dry dicot leaf litter. The model was fitted using generalized linear mixed-effects model using Poisson error structure.

opencc-by-4.0Jun 2017View details →

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