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zenodo28/100

Figure 2 in Temporal dynamics of invertebrate and aquatic plant communities at three intermittent ponds in livestock grazed Patagonian wetlands

Figure 2. Seasonal variation of particulate organic matter (POM, dashed lines) and aquatic plant coverage (solid line) at three ponds on a Patagonian steppe wetland (Argentina) during the study period (May 2008 to April 2009). Categories of aquatic plant coverage explained in methodology. Livestock stocking period is indicated in the figure (black bar).

opencc-by-4.0Aug 2015View details →
zenodo28/100

Figure 1 in Temporal dynamics of invertebrate and aquatic plant communities at three intermittent ponds in livestock grazed Patagonian wetlands

Figure 1. (A) Location of the sampling sites (P1, P2 and P3) at Mallín Crespo (Chubut Province, Patagonia, Argentina) during connected (June–December) and hydrologically isolated (January–May) periods. The three ponds are in the same scale. (B) Daily rain (dashed line) and mean daily air temperature (solid line), from May 2008 to April 2009. (C–E) Physicochemical variables sampled monthly and once per pond. Dashed line (D), indicates unavailable data.

opencc-by-4.0Aug 2015View details →
zenodo28/100

Figure 1 in Identification of New World aquatic invertebrate illustrations in The Drake Manuscript

Figure 1. (Continued) (B) Lindapecten muscosus (Wood, 1828) rough scallop, © Guido and Philippe Poppe. Reproduced by permission of Guido and Philippe Poppe www.conchology. be); (C) Pinctada imbricate Röding, 1798 Atlantic pearl-oyster, © Guido and Philippe Poppe. Reproduced by permission of Guido and Philippe Poppe (www.conchology.be); (D) Crassostrea virginica (Gmelin, 1791) eastern oyster, © Reuben Goforth. Reproduced by permission of Reuben Goforth; (E) Solena obliqua (Spengler, 1794) oblique jackknife, © Association Française de Conchyliologie. Reproduced by permission of Association Française de Conchyliologie (www.xenophora.org); (F) unknown unionid clam with image of Lampsilis reeveiana for comparison, © Chris Barnhart. Reproduced by permission of Chris Barnhart ChrisBarnhart@MissouriState.edu); (G) Atrina rigida (Lightfoot, 1786) stiff pen shell, © Jon Fajans. Reproduced by permission of Jon Fajans, Online Resource Guide for Florida Shellfish Aquaculture (http://shellfish.ifas.ufl.edu). Permission to reuse the images must be obtained from the rightsholder.

opencc-by-4.0Apr 2014View details →
zenodo28/100

Figure 1 in Identification of New World aquatic invertebrate illustrations in The Drake Manuscript

Figure 1. Illustrations of molluscs in The Drake Manuscript (left), © The Morgan Library & Museum, New York. Corresponding contemporary images of the species (right) proposed to be the subjects of the anonymous artist's illustrations. Mollusc species include (A) Nodipecten nodosus (Linnaeus, 1758) lions-paw scallop, © Caledonian Seashells. Reproduced by permission of Caledonian Seashells (www.caledonianseashells. com).

opencc-by-4.0Apr 2014View details →
zenodo28/100

Figure 4 in Identification of New World aquatic invertebrate illustrations in The Drake Manuscript

Figure 4. Illustrations of horseshoe crab (Limulus polyphemus) and land crab (Cardisoma guanhumi) taken from: (A) painting ca. 1585 by John White entitled 'Indians Fishing' showing horseshoe crab in the lower right, © Trustees of the British Museum. Reproduced by permission of The British Museum; (B) engraving of Theodore De Bry of 1590 after White showing horseshoe crab and land crab, reproduced by permission of The Huntington Library, San Marino, California; (C) land crab in a painting by John White, © Trustees of the British Museum. Reproduced by permission of The British Museum; (D) engraving of horseshoe crab in a 1613 map of New France drawn by David Pelletier from sketches of Samuel de Champlain labelled siguenoc © V. Dickinson. Reproduced by permission of V. Dickinson. Permission to reuse images be obtained from the rightsholder.

opencc-by-4.0Apr 2014View details →
dryad28/100

Data from: Does the aquatic invertebrate nipple array prevent bubble adhesion?: an experiment using nanopillar sheets

The nipple array is a submicron-scale structure found on the cuticle surfaces of various invertebrate taxa. Corneal nipples are an antiglare surface in nocturnal insects, but the functional significance of the nipple array has not been experimentally investigated for aquatic organisms. Using nanopillar sheets as a mimetic model of the nipple array, we demonstrated that significantly fewer bubbles adhered to the nanopillar surface versus a flat surface when the sheets were hydrophilic. Many more bubbles adhered to the hydrophobic surface than the hydrophilic surfaces. Bubbles on the body surface may cause buoyancy problems, movement interference and water flow occlusion. Here, bubble repellence is proposed as a function of the hydrophilic nipple array in aquatic invertebrates and the properties are considered based on bubble adhesion energy.

opencc-zeroDec 2012View details →
dryad28/100

Data from: Multielement stoichiometry in aquatic invertebrates: when growth dilution matters

Element concentrations in organisms can be variable, often causing deviations from otherwise consistent, taxon-specific multielement stoichiometries. Such variation can have considerable ecological consequences, yet physiological mechanisms remain unclear. We tested the influence of somatic growth dilution (SGD) on multiple element concentrations under different bioenergetic conditions. SGD occurs when rapid individual growth causes a disproportional gain in biomass relative to gain of a specific element. SGD can strongly affect elements in various organisms, but we lack a general framework to unify results across studies and assess its overall importance. We derived the general conditions that trigger SGD from an element accumulation model. We parameterized the model with bioenergetic and element-specific rates summarized from the literature to compare SGD effects on 15 elements (nonessential metals, essential trace elements, macronutrients) in three aquatic invertebrate taxa. For all taxa, we found that SGD: (1) occurs to some degree for all 15 elements over realistic ranges of growth and ingestion rates, and (2) has the greatest effect on elements with low efflux (excretion) rates, including certain nonessential metals (e.g., MeHg, Po), essential trace elements and macronutrients (e.g., N, Fe). Thus, SGD can strongly affect concentrations of a spectrum of elements under natural conditions. These results provide a framework for predicting variation in elemental composition of animals.

opencc-zeroDec 2009View details →
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Data from: Genetic divergence and isolation by thermal environment in geothermal populations of an aquatic invertebrate

[No abstract entered]

opencc-zeroDec 2015View details →
zenodo28/100

Figure 6 from: Chertoprud ES, Palatov DM, Borisov RR, Marinskiy VV, Bizin MS, Dbar RS (2016) Distribution and a comparative analysis of the aquatic invertebrate fauna in caves of the western Caucasus. Subterranean Biology 18: 49-70. https://doi.org/10.3897/subtbiol.18.8648

Figure 6 - Spatial variations in relative abundance of main invertebrates groups along the gradient of subterranean environmental conditions. (X-axis: 0 — the cave entrance area, negative values — epigean zone, positive values — cave zone). A Cave Abrskila B Cave Golova Otapa.

opencc-by-4.0Jun 2016View details →
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Figure 1 from: Chertoprud ES, Palatov DM, Borisov RR, Marinskiy VV, Bizin MS, Dbar RS (2016) Distribution and a comparative analysis of the aquatic invertebrate fauna in caves of the western Caucasus. Subterranean Biology 18: 49-70. https://doi.org/10.3897/subtbiol.18.8648

Figure 1 - Map of the study regions of Abkhazia. Caves: 1 New Athos 2 Simona Kananita 3 Nizhnyaya Shakuranskaya 4 Srednyaya Shakuranskaya 5 Tsebel'dinskaya 6 Abrskila 7 Golova Otapa 8 Well Uapatyh 9 Well 85 m.

opencc-by-4.0Jun 2016View details →
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Figure 3 from: Chertoprud ES, Palatov DM, Borisov RR, Marinskiy VV, Bizin MS, Dbar RS (2016) Distribution and a comparative analysis of the aquatic invertebrate fauna in caves of the western Caucasus. Subterranean Biology 18: 49-70. https://doi.org/10.3897/subtbiol.18.8648

Figure 3 - Map of Cave Golova Otapa. Sampling stations marked by red points (accordingly Grigorjan 1973).

opencc-by-4.0Jun 2016View details →
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Figure 2 from: Chertoprud ES, Palatov DM, Borisov RR, Marinskiy VV, Bizin MS, Dbar RS (2016) Distribution and a comparative analysis of the aquatic invertebrate fauna in caves of the western Caucasus. Subterranean Biology 18: 49-70. https://doi.org/10.3897/subtbiol.18.8648

Figure 2 - Map of Cave Abrskila. Sampling stations marked by red points (accordingly Benze et al. 1965).

opencc-by-4.0Jun 2016View details →
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Figure 5 from: Chertoprud ES, Palatov DM, Borisov RR, Marinskiy VV, Bizin MS, Dbar RS (2016) Distribution and a comparative analysis of the aquatic invertebrate fauna in caves of the western Caucasus. Subterranean Biology 18: 49-70. https://doi.org/10.3897/subtbiol.18.8648

Figure 5 - Spatial variations in abundance and species richness of the fauna along the gradient of subterranean environmental conditions. (X-axis: 0 — the cave entrance area, negative values — epigean zone, positive values — cave zone). A Cave Abrskila B Cave Golova Otapa.

opencc-by-4.0Jun 2016View details →
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Figure 4 from: Chertoprud ES, Palatov DM, Borisov RR, Marinskiy VV, Bizin MS, Dbar RS (2016) Distribution and a comparative analysis of the aquatic invertebrate fauna in caves of the western Caucasus. Subterranean Biology 18: 49-70. https://doi.org/10.3897/subtbiol.18.8648

Figure 4 - Map of Cave New Athos. Sampling stations marked by red points (accordingly Abhastur 2009).

opencc-by-4.0Jun 2016View details →
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Figure 7 from: Chertoprud ES, Palatov DM, Borisov RR, Marinskiy VV, Bizin MS, Dbar RS (2016) Distribution and a comparative analysis of the aquatic invertebrate fauna in caves of the western Caucasus. Subterranean Biology 18: 49-70. https://doi.org/10.3897/subtbiol.18.8648

Figure 7 - Two-dimensional ordination with superimposed clusters of the stygobiotic faunas from different caves, based on Kulszinski similarity index. River valleys are shown by different colors. Caves: 1 New Athos 2 Simona Kananita 3 Nizhnyaya Shakuranskaya 4 Srednyaya Shakuranskaya 5 Tsebel'dinskaya 6 Abrskila 7 Golova Otapa 8 Well Uapatyh 9 Well 85 m.

opencc-by-4.0Jun 2016View details →
zenodo28/100

Fig. 6 in Aquatic invertebrate communities of perennial pans in Mpumalanga, South Africa: a diversity and functional approach

Fig. 6. RDA plot showing the similarity among sites during the different seasons, based on the various community traits (metrics) with physico-chemical variables superimposed. This tri-plot describes 56.2 % of the variation in the data, where 38.6 % is displayed on the first axis and 17.6 % on the second axis. Only metrics of which more than 31 % is explained by the model and the 14 most significant variables are visualised.

opencc-by-4.0Dec 2012View details →
dryad28/100

Data from: Multielement stoichiometry in aquatic invertebrates: when growth dilution matters

Open the record for dataset details and reuse information.

publicAug 2010View details →
dryad28/100

Data from: Artificial agri-environment scheme ponds do not replicate natural environments despite higher aquatic and terrestrial invertebrate richness and abundance

Open the record for dataset details and reuse information.

publicAug 2020View details →
dryad28/100

Data from: Differential response to heat-stress among evolutionary lineages of an aquatic invertebrate species complex

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publicNov 2018View details →
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Data from: Does the aquatic invertebrate nipple array prevent bubble adhesion?: an experiment using nanopillar sheets

Open the record for dataset details and reuse information.

publicAug 2013View details →

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