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22 results for “Heraklion”
Data from Phenocam (PHE) measurements at Heraklion – FORTH (HEFORT) from 2023-03-24 to 2023-12-31 [RAW]
<p>Original phenocam images separated into near-infrared (NIR) and visible (VIS).</p>
Fig. A4 in Trace metal concentrations in the offshore surficial sediments of Heraklion Gulf (Crete Island, East Mediterranean Sea) Abstract
Fig. A4: Cr (total, nlh and %nlh) per transect [transects are presented from west to east, (•) the outlier value symbol and numbers refer to the isobaths].
Fig. A3 in Trace metal concentrations in the offshore surficial sediments of Heraklion Gulf (Crete Island, East Mediterranean Sea) Abstract
Fig. A3: Mn (total, nlh and %nlh) per transect [transects are presented from west to east, (•) the outlier value symbol and numbers refer to the isobaths].
Fig. A5 in Trace metal concentrations in the offshore surficial sediments of Heraklion Gulf (Crete Island, East Mediterranean Sea) Abstract
Fig. A5: Total Cu, Pb and Zn and nlhZn per transect [transects are presented from west to east, (•) the outlier value symbol and numbers refer to the isobaths].
Fig. A2 in Trace metal concentrations in the offshore surficial sediments of Heraklion Gulf (Crete Island, East Mediterranean Sea) Abstract
Fig. A2: Al and Fe (total, nlh and %nlh) per transect [transects are presented from west to east, (•)the outlier value symbol and numbers refer to the isobaths].
Fig. 8 in Trace metal concentrations in the offshore surficial sediments of Heraklion Gulf (Crete Island, East Mediterranean Sea) Abstract
Fig. 8: Map showing the sampling stations in 1989 (referred by Poulos et al., 2009) (·) and those of the present investigation (x) over the bathymetry.
Fig. 7 in Trace metal concentrations in the offshore surficial sediments of Heraklion Gulf (Crete Island, East Mediterranean Sea) Abstract
Fig. 7: Spatial distribution of non-lattice held (nlh) metals in surficial seabed sediments (a: Fe; b: Zn; c: Mn; d: Cr).
Fig. 6 in Trace metal concentrations in the offshore surficial sediments of Heraklion Gulf (Crete Island, East Mediterranean Sea) Abstract
Fig. 6: Spatial distribution of total metal content in sediments (Al distribution is not presented, as it is similar to Fe) [a: Fe; b: Zn; c: Pb; d: Mn; e: Cu; f: Cr].
Fig. 5 in Trace metal concentrations in the offshore surficial sediments of Heraklion Gulf (Crete Island, East Mediterranean Sea) Abstract
Fig. 5: (a): Carbonate content box plots grouped by percent silt+clay, b) Carbonate content box plots per transect (west to east) [(•) outlier value symbol, (*) extreme value symbol, numbers refer to the isobaths].
Fig. 4 in Trace metal concentrations in the offshore surficial sediments of Heraklion Gulf (Crete Island, East Mediterranean Sea) Abstract
Fig. 4(a): Particulate Organic Carbon (POC) values box-plot grouped by percent silt+clay; (b): Particulate Organic Carbon (POC) values box-plot per transect (from west to east) [(•) outlier value symbol, numbers refer to the isobaths].
Fig. 3 in Trace metal concentrations in the offshore surficial sediments of Heraklion Gulf (Crete Island, East Mediterranean Sea) Abstract
Fig. 3: Texture map based on grain size analysis according to Folk 1974. [gmS: gravelly muddy Sand; S: Sand; zS: silty Sand; sZ: sandy Silt; Z:Silt; C: Clay; M: Mud (=silt+clay) and hc: closure depth in red].
Fig. 2 in Trace metal concentrations in the offshore surficial sediments of Heraklion Gulf (Crete Island, East Mediterranean Sea) Abstract
Fig. 2: Determination of the offshore zone (blue zone) by means of L/4 (according to Komar, 1976) for approaching waves of different wave lengths (L). Closure depth limit (hc) is also presented (12 m isobath).
Fig. 1 in Trace metal concentrations in the offshore surficial sediments of Heraklion Gulf (Crete Island, East Mediterranean Sea) Abstract
Fig. 1: Location map showing the bathymetry (in metres), sampling stations (1-55), river/torrent mouths (from west to east: a-Almiros, b-Gazanos, c-Xiropotamos, d-Giofyros, e- Krateros, f-Vathilagkos, g-Gournianos, h-Gouvianos, i-Aposelemis, j-Sfakoryako) and the most important potential terrestrial sources of pollution (1: oil storages; 2: Electric Power Station; 3: outfall of treated waste water; 4: former outfall of untreated waste water; and 5: former Gouves military base).
Black Bull - Heraklion Archaeological Museum
So draft test model Source: Objaverse 1.0 / Sketchfab
Supplementary material 1 from: Papastefanou G, Panayiotou E, Mylonas M, Simaiakis SM (2015) Centipede assemblages along an urbanization gradient in the city of Heraklion, Crete (Greece). In: Tuf IH, Tajovský K (Eds) Proceedings of the 16th International Congress of Myriapodology, Olomouc, Czech Republic. ZooKeys 510: 163-179. https://doi.org/10.3897/zookeys.510.8414
Abundance and activity density of centipede species per sampling site.: Explanation note: List of species and individuals captured at each sampling site.
Fig. A1 in Trace metal concentrations in the offshore surficial sediments of Heraklion Gulf (Crete Island, East Mediterranean Sea) Abstract
Fig. A1: Schematic presentation of sand, silt, clay distribution and Particulate Organic Carbon (POC) percentages.
Figure 4 from: Papastefanou G, Panayiotou E, Mylonas M, Simaiakis SM (2015) Centipede assemblages along an urbanization gradient in the city of Heraklion, Crete (Greece). In: Tuf IH, Tajovský K (Eds) Proceedings of the 16th International Congress of Myriapodology, Olomouc, Czech Republic. ZooKeys 510: 163-179. https://doi.org/10.3897/zookeys.510.8414
Figure 4 - NMDS two-dimensional ordination plot based on the Bray-Curtis dissimilarity matrix of the nine sites along the urbanization gradient.
Figure 6 from: Papastefanou G, Panayiotou E, Mylonas M, Simaiakis SM (2015) Centipede assemblages along an urbanization gradient in the city of Heraklion, Crete (Greece). In: Tuf IH, Tajovský K (Eds) Proceedings of the 16th International Congress of Myriapodology, Olomouc, Czech Republic. ZooKeys 510: 163-179. https://doi.org/10.3897/zookeys.510.8414
Figure 6 - Total and average abundance of all four generalist species as well as average abundance of each generalist species along the urban-rural gradient, Eupolybothrus litoralis (♦), Lithobius nigripalpis (▲), Scolopendra cretica (■), Scutigera coleoptrata (●). White columns show total abundance, grey columns show average abundance with bars with standard deviation.
Figure 3 from: Papastefanou G, Panayiotou E, Mylonas M, Simaiakis SM (2015) Centipede assemblages along an urbanization gradient in the city of Heraklion, Crete (Greece). In: Tuf IH, Tajovský K (Eds) Proceedings of the 16th International Congress of Myriapodology, Olomouc, Czech Republic. ZooKeys 510: 163-179. https://doi.org/10.3897/zookeys.510.8414
Figure 3 - Species accumulation curves (recorded as a function of sampling effort) of the rate at which new species are found within each site along the urbanization gradient.
Figure 2 from: Papastefanou G, Panayiotou E, Mylonas M, Simaiakis SM (2015) Centipede assemblages along an urbanization gradient in the city of Heraklion, Crete (Greece). In: Tuf IH, Tajovský K (Eds) Proceedings of the 16th International Congress of Myriapodology, Olomouc, Czech Republic. ZooKeys 510: 163-179. https://doi.org/10.3897/zookeys.510.8414
Figure 2 - Total and average abundance of centipedes as well as total species richness along the urban-rural gradient. White columns show total abundance, grey columns show average abundance with bars with standard deviation, dark line shows species richness.
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Allen Brain Atlas
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International Brain Laboratory public data
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OpenNeuro
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