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385 results for “Shading”
Long term response of arctic tussock tundra to thermal erosion features: A modeling analysis. Tussock tundra shade house simulation
The Multiple Element Limitation (MEL) model is used to simulate the recovery of Alaskan arctic tussock tundra to thermal erosion features (TEFs) caused by permafrost thaw and mass wasting. TEFs could be significant to regional carbon (C) and nutrient budgets because permafrost soils contain large stocks of soil organic matter (SOM) and TEFs are expected to become more frequent as climate warms. These simulations deal only with recovery following TEF stabilization and do not address initial losses of C and nutrients during TEF formation. To capture the variability among and within TEFs, we simulate a range of post-stabilization conditions by varying the initial size of SOM pools and nutrient supply rates. This file contains the results for 25 years of tussock tundra under shade conditions.
Effects of shading on tundra vegetation senescence at Toolik Lake, Coldfoot, Sagwon - Alaska 2016
Data on the effects of shading tundra vegetation from the sun when it is low in on the horizon in the north. If light quality was altered through shading, phenology might be affected. Senescence (color change) was measured for the common tundra species.
Effects of intercropping on the herbage production of a binary grass-legume mixture (Hedisarum coronarium L. and Lolium multiflorum Lam.) under artificial shade in Mediterranean rainfed conditions
<p>This dataset refers to the experimental raw data (csv version) collected within the trial reported in the concerned article on the following parameters:</p> <p>1. crop aboveground biomass, splitted per field, mowing, crop, treatment and replicate (crop aboveground biomass.csv)</p> <p>2. cumulated crop aboveground biomass, splitted per field, year, crop, treatment and replicate (cumulated crop aboveground biomass_year.csv)</p> <p>3. cumulated crop aboveground biomass for the two years of the growing cycle, splitted per field, crop, treatment and replicate (cumulated crop aboveground biomass_2years.csv)</p> <p>4. partial and total RYT splitted per year, field and treatment (RYT_year)</p> <p>5. partial and total RYT for the two years of the growing cycle, splitted per field and treatment (RYT_2years)</p> <p> </p> <p><br> </p>
Annual summer single-day measurements of the thermal environment with a bio-meteorological sensor under trees, shade structures, and sun-exposed areas in the Rio Salado Park in Tempe, AZ, USA
We have measured the thermal environment/bio-meteorological conditions under trees, shade structures, and at sun-exposed locations in the Rio Salado Park in Tempe, AZ, USA annually since 2018 on a clear sky, hot, sunny day in June/July to track shade performance of newly planted trees over time. Measurements were taken with a mobile bio-meteorological weather station, known as MaRTy (Middel & Krayenhoff, 2019; DOI: 10.1016/j.scitotenv.2019.06.085). Since the measurement campaign began, some of the trees have died, were removed, or their environment has changed due to external events such as a bridge collapse (2020-07-29).
Modeled riparian stream shading: Agreement with field measurements and sensitivity to riparian conditions
Data was collected from relatively straight channel segments in eight stream and river segments ranging from 12 to 43 meters wide in Clarke County, GA in 2008. Only channels wide enough to feature a canopy gap between the overhanging tree branches were selected. Within each stream segment stream azimuth, latitude and longitude, riparian tree height, bankfull channel width, bank height, canopy overhang height, and measurements of canopy cover with a densiometer were collected. Time and date of collections were recorded.
Datasets for Background and Shading Correction of Optical Microscopy Images by BaSiC -- Downsampled Version
<p>This repository holds downsampled example data for publication: "<strong>A BaSiC tool for background and shading correction of optical microscopy images, Nature Communications (2017)</strong>" DOI: <a href="https://doi.org/10.1038/ncomms14836">https://doi.org/10.1038/ncomms14836</a>. For full-resolution testing data, please refer to Zenodo repository at DOI: <a href="https://zenodo.org/record/6334810#.YvD6zHZBxD8">10.5281/zenodo.6334810</a>.</p>
Shape from Shading Digital Elevation Model for Oxia Planum Candidate Landing Site
<p>This data set contains the calibrated and map-projected HiRISE image ESP_037558_1985 and the matching Shape from Shading DEM using the method described in Hess et al., (2019a), and in more detail in Hess et al. (2022). The SfS DTM was part of the EPSC abstract Hess et al., (2019b). When using the data please reference Hess et al. (2022) for the method.</p> <p>ESP_037558_1985_30cm_o.cub: Image data in radiances, ISIS cube file, Equirectangular map projection at 0.25 m/pixel resolution.</p> <p>ESP_037558_1985_30cm_DEM.cub: Digital Elevation Model (DEM) with heights in meter, ISIS cube file, Equirectangular map projection at 0.25 m/pixel resolution.</p> <p>Cube files can be converted to other data formats using gdal (https://gdal.org/) or directly loaded in, e.g., ArcGIS or QGIS.</p> <p> </p> <p>Hess, M., Wohlfarth, K., Grumpe, A., Wöhler, C., Ruesch, O., and Wu, B.: ATMOSPHERICALLY COMPENSATED SHAPE FROM SHADING ON THE MARTIAN SURFACE: TOWARDS THE PERFECT DIGITAL TERRAIN MODEL OF MARS, Int. Arch. Photogramm. Remote Sens. Spatial Inf. Sci., XLII-2/W13, 1405–1411, https://doi.org/10.5194/isprs-archives-XLII-2-W13-1405-2019, 2019a.</p> <p>Hess, Marcel. "High Resolution Digital Terrain Model for the Landing Site of the Rosalind Franklin (ExoMars) Rover." Proc. European Planetary Science Congress, EPSC-DPS2019-1533-4, Geneva, Switzerland, 2019b.</p> <p>Hess, M.; Tenthoff, M.; Wohlfarth, K.; Wöhler, C. Atmospheric Correction for High-Resolution Shape from Shading on Mars. <em>J. Imaging</em> <strong>2022</strong>, <em>8</em>, 158. https://doi.org/10.3390/jimaging8060158</p>
Evaluating the impact of shade on Nitrogen fixation in sulla (Hedysarum coronarium L.): a 15N natural abundance study
<p>This dataset refers to the experimental raw data (csv version) collected within the trial reported in the concerned article on the following parameters:</p> <p>1. total nitrogen, delta N15, nitrogen derived from atmosphere, root biomass, nitrogen yield, nitrogen fixed, splitted per experiment, mowing, crop, treatment and replicate (15N_root.csv).</p> <p>2. total nitrogen, delta N15, nitrogen derived from atmosphere, shoot biomass, nitrogen yield, nitrogen fixed, splitted per experiment, mowing, crop, treatment and replicate (15N_shoot.csv).</p> <p>3. shoot cumulative nitrogen yield, root cumulative nitrogen yield, shoot cumulative nitrogen fixed, root cumulative nitrogen fixed, shoot:root ratio of nitrogen yield, shoot:root ratio of nitrogen fixed, splitted per experiment, treatment and replicate (shoot root ratio and N cumulative value.csv).</p>
Data from: Habitat selection in transformed landscapes and the role of forest remnants and shade coffee in the conservation of resident birds
1. Biodiversity conservation in transformed landscapes is becoming increasingly important. However, most assessments of the value of modified habitats rely heavily on species presence and/or abundance, masking ecological processes such as habitat selection and phenomena like ecological traps, which may render species persistence uncertain. High species richness has been documented in tropical agroforestry systems but comparisons with native habitat remnants generally lack detailed information on species demography and habitat use. 2. We generated a multi-species, multi-measure framework to evaluate the role of habitat selection in the adaptation of species to transformed landscapes, and demonstrate that its use could affect how we value the contribution different land uses make to biodiversity conservation. 3. We analyzed seven years of capture-mark-recapture and observation data for twelve species of resident birds present in native forest remnants and shade coffee plantations in a mega-diverse region. We assessed whether species behaved adaptively by evaluating the correlation between measures of habitat preference (occurrence, abundance, fidelity, inter-seasonal variance and age) and performance (body condition, muscle, primary molt, breeding and juveniles) in forest and coffee, and generated hypotheses about their role in species persistence. 4. We documented adaptive habitat selection for seven species, non-ideal selection for four, and maladaptive selection for one. While many species showed equal-preference and/or equal performance in many traits, in general we found more evidence for birds preferring and/or performing better in forest than coffee, although relationships between our indicators and population adaptation need to be studied further before our proposed framework can be applied to more species and landscapes. 5. While shade coffee can act as a biodiversity-friendly matrix providing complementary or supplementary habitat to a wide range of resident bird species, protecting remnants of native vegetation is still of paramount importance for biodiversity conservation in agricultural landscapes. 28-Aug-2019
Impact of spatio-temporal shade dynamics on winter wheat growth and yield
<p>During two growing seasons (2013-2014, 2014-2015), an artificial shade structure was installed on the experimental farm of Gembloux Agro-Bio Tech to evaluate winter wheat growth, productivity and quality under shade. During both seasons, global radiation (MJ/m²/days) at crop canopy level was measured with quantum sensors (CS300- Campbell Scientific Inc., USA – accuracy ± 5 % for the daily global radiation) and recorded every minute by a data logger (CR1000 - Campbell Scientific Inc., USA). These data are compiled at a daily time scale for each treatment (CS: constant shade, PS: periodic shade, NS: no shade) into the tables “<em>GR_2013_2014.txt</em>” and “<em>GR_2014_2015.txt</em>”.</p> <p>During the cropping season, we sampled winter wheat to assess aboveground biomass, dry matter dynamics, final yield, yield components (thousand grain yield, grain size, and spike per m²) and grain protein content. These data are compiled in the two tables “<em>sampling_2013_2014.txt</em>” and “<em>sampling_2014_2015.txt</em>”. Samples were taken from three adjacent sowing lines of 40 cm. To assess dry matter distribution (g/m²), wheat plants were subdivided into spikes (<em>DM_Spike_g_m2</em>) and straw (<em>DM_Straw_g_m2</em>), dried and weighed. The final yield is expressed in t/ha at 0% humidity (<em>Yield_t_ha_0%</em>). We assessed the proportion of grain size using 3 sieves: 2.2, 2.5, 2.8 mm (<em>Grain_weight_seive_2.2mm, Grain_weight_seive_2.5mm, Grain_weight_seive_2.8mm</em>). Thousand grain weight at 0% humidity was calculated on subsamples from the harvested plots (<em>TGW_g_0%</em>). Protein content (%) analysis was performed with near-infrared reflectance spectroscopy technique (<em>Protein_content_%).</em></p> <p>Detailed information on the experimental design will be available in the following paper: “Impact of spatio-temporal shade dynamics on wheat growth and yield, perspectives for temperate agroforestry” in European Journal of Agronomy.</p>
Data from: Thinning and prescribed burning increase shade-tolerant conifer regeneration in a fire excluded mixed-conifer forest
<p>Fire exclusion and past management have altered the composition, structure, and function of frequent-fire forests throughout western North America. In mixed-conifer forests of the California Sierra Nevada, fire exclusion has exacerbated the effects of drought and endemic bark beetles, resulting in extensive mortality of fire-adapted pine species. Thinning and prescribed fire are widely used in these forests to reduce fuels, moderate fire behavior, and restore ecosystems. Tree regeneration influences future forest composition and structure, and therefore future resilience to disturbances, but long-term effects of thinning and prescribed burning on tree regeneration after prolonged fire exclusion are poorly understood. We measured tree regeneration one year prior to, and periodically for 16 years following thinning and prescribed burning in a mixed-conifer forest in the Sierra Nevada, California, USA. We asked three questions. How did the composition and density of tree regeneration change after thinning and prescribed burning? Did pretreatment vegetation types influence conifer regeneration density after treatments? Did planting after overstory thinning increase regeneration density of native pine species?</p> <p>Sixteen years after treatments, combined natural regeneration of shade-tolerant white fir (Abies concolor) and incense-cedar (<em>Calocedrus</em> <em>decurrens</em>) averaged 2,032 trees per hectare (tph) after understory thinning, and 7,745 tph after understory thinning combined with prescribed burning, increases of 37% and 146% from pretreatment densities. In contrast, combined natural regeneration of white fir and incense-cedar averaged 497 tph after overstory thinning, 780 tph after overstory thinning with prescribed burning, 113 tph after prescribed burning alone, and 807 tph in untreated controls, all of which were declines from pretreatment densities. Natural regeneration of white fir and incense-cedar was consistently an order of magnitude greater than Jeffrey pine (<em>Pinus</em> <em>jeffreyi</em>) and sugar pine (<em>Pinus</em> <em>lambertiana</em>), whose combined densities 16 years after treatments averaged 37 tph across treatments and did not significantly respond to thinning and/or prescribed burning. Natural conifer regeneration after treatments varied by pre-treatment vegetation type (closed canopy, <em>Ceanothus</em> <em>cordulatus</em> shrub-dominated, and open sparse), with large increases of natural regeneration after understory thinning in closed canopy and <em>Ceanothus</em> shrub vegetation types. Planting increased sugar pine regeneration density after overstory thinning, marginally increased Jeffrey pine regeneration after overstory thinning combined with prescribed burning, and increased white fir regeneration after overstory thinning with and without burning. No treatments reduced white fir and incense-cedar natural regeneration while simultaneously increasing natural pine regeneration, suggesting new thinning, burning, and planting approaches may be required to meet regeneration restoration objectives.</p>
Effect of shade and nitrogen content on Arabidopsis Col-0 and cytokinin mutants abcg14 and cypDM mRNA-seq gene expression processed tables.
<p>This dataset is an add-on for Gautrat et al., containing processed files for the mRNAseq data in tab delimited txt format.</p> <p>Here, you can obtain the raw counts file, the normalized CPM values, and the normalized logCPM values</p> <p>The RNA-seq raw data supporting the conclusions of this article have been deposited in ArrayExpress (Kolesnikov et al., 2015) at EMBL-EBI (www.ebi.ac.uk/arrayexpress), under accession numbers E-MTAB-13638.</p> <p>All relevant custom r scripts are available at https://github.com/aromanowski/shade_N_ck</p>
FIG. 12 in Fifty shades of white: morphological and molecular diversity of the Cadlina laevis species complex (Gastropoda: Nudibranchia) in the North-West Pacific
FIG. 12. Penial morphology in Cadlina spp. A. Cadlina sp. 3, MIMB47975. B. Cadlina umiushi, MIMB47996. C. Cadlina laevis, MIMB47963. Scale bars: A, C = 100 µm; A', B' = 50 µm; C = 200 µm; C' = 20 µm. РИС. 12. МорфологиЯ пениса Cadlina spp. A. Cadlina sp. 3, MIMB47975. B. Cadlina umiushi, MIMB47996. C. Cadlina laevis, MIMB47963. Масштабные линейки: A, C = 100 мкм; A', B' = 50 мкм; C = 200 мкм; C' = 20 мкм.
FIG. 11 in Fifty shades of white: morphological and molecular diversity of the Cadlina laevis species complex (Gastropoda: Nudibranchia) in the North-West Pacific
FIG. 11. Configuration of male and female reproductive organs in Cadlina spp., female gland mass removed. A. Cadlina laevis, MIMB47963. B. Cadlina umiushi, MIMB47996. C. Cadlina sp. 3, MIMB47975. D. Cadlina sp. 4, MIMB47978. E. Cadlina sp. 1, MIMB47971. F. Cadlina sp. 7, MIMB47981. G. Cadlina sp. 6, MIMB47980. Abbreviations: amp = ampulla; bc = bursa copulatrix; ps = penial sheath; pvd = prostatic vas deferens; rs = receptaculum seminis; va = vagina. Scale bar: 1 mm. РИС. 11. МорфологиЯ муЖских и Женских репродуктивных органов Cadlina spp., комплекс Женских ЖелеЗ удален. A. Cadlina laevis, MIMB47963. B. Cadlina umiushi, MIMB47996. C. Cadlina sp. 3, MIMB47975. D. Cadlina sp. 4, MIMB47978. E. Cadlina sp. 1, MIMB47971. F. Cadlina sp. 7, MIMB47981. G. Cadlina sp. 6, MIMB47980. СокраЩениЯ: amp = ампулла; bc = копулЯтивнаЯ сумка; ps = мешок пениса; pvd = простатический семЯпровод; rs = семЯприемник; va = вагина. МасштабнаЯ линейка: 1 мм.
FIG. 10 in Fifty shades of white: morphological and molecular diversity of the Cadlina laevis species complex (Gastropoda: Nudibranchia) in the North-West Pacific
FIG. 10. Buccal armature of Cadlina umiushi from the Sea of Japan (SEM). A. MIMB47995, radula. B. MIMB47995, anterior radular portion, rachidian and inner lateral teeth. C. MIMB47995, outer lateral teeth. D. MIMB47995, radula on odontophore. E. MIMB47995, labial cuticle. F. MIMB47995, labial cuticle elements. G. MIMB47996, radula. H. MIMB47996, rachidian and innermost lateral teeth. I. MIMB47996, outer lateral teeth. Scale bars: A = 500 µm; B, C, I = 50 µm; D, E, G = 200 µm; F = 10 µm; H = 20 µm. РИС. 10. Буккальное вооруЖение Cadlina umiushi иЗ Японского морЯ (СЭМ). А. MIMB47995, радула. B. MIMB47995, переднЯЯ часть радулы, центральные и внутренние латеральные Зубы. С. MIMB47995, внешние латеральные Зубы. D. MIMB47995, радула на одонтофоре. Е. MIMB47995, лабиальнаЯ кутикула. F. MIMB47995, Элементы лабиальной кутикулы. G. MIMB47996, радула. H. MIMB47996, центральные и внутренние латеральные Зубы. I. MIMB47996, внешние латеральные Зубы. Масштабные линейки: A = 500 мкм; B, C, I = 50 мкм; D, E, G = 200 мкм; F = 10 мкм; Н = 20 мкм.
FIG. 9 in Fifty shades of white: morphological and molecular diversity of the Cadlina laevis species complex (Gastropoda: Nudibranchia) in the North-West Pacific
FIG. 9. Buccal armature of Cadlina sp. 6 (MIMB47980, Shikotan Is., Sea of Okhotsk) and Cadlina sp. 5 (MIMB47979, Iturup Is., Sea of Okhotsk) (SEM). A. Cadlina sp. 6, anterior radular portion. B. Cadlina sp. 6, rachidian and inner lateral teeth. C. Cadlina sp. 6, rachidian and innermost lateral teeth. D. Cadlina sp. 6, middle radular portion. E. Cadlina sp. 6, outer lateral teeth. F. Cadlina sp. 6, rachidian and innermost lateral teeth. G. Cadlina sp. 6, radula on odontophore. H. Cadlina sp. 6, labial cuticle. I. Cadlina sp. 6, labial cuticle elements. J. Cadlina sp. 5, radula. K. Cadlina sp. 5, rachidian and inner lateral teeth. L. Cadlina sp. 5, rachidian teeth. M. Cadlina sp. 5, outer lateral teeth. N. Cadlina sp. 5, radula on odontophore. O. Cadlina sp. 5, labial cuticle. P. Cadlina sp. 5, labial cuticle rodlets. Scale bars: A, N, O = 100 µm; B, E, M = 50 µm; C, F, I, L = 10 µm; D, G, H, J = 200 µm; K, P = 20 µm. РИС. 9. Буккальное вооруЖение Cadlina sp. 6 (MIMB47980, о. Шикотан, Охотское море) и Cadlina sp. 5 (MIMB47979, о. Итуруп, Охотское море) (СЭМ). A. Cadlina sp. 6, переднЯЯ часть радулы. B. Cadlina sp. 6, центральные и внутренние латеральные Зубы. C. Cadlina sp. 6, центральные и внутренние латеральные Зубы. D. Cadlina sp. 6, среднЯЯ часть радулы. E. Cadlina sp. 6, внешние латеральные Зубы. F. Cadlina sp. 6, центральные и внутренние латеральные Зубы. G. Cadlina sp. 6, радула на одонтофоре. H. Cadlina sp. 6, лабиальнаЯ кутикула. I. Cadlina sp. 6, Элементы лабиальной кутикулы. J. Cadlina sp. 5, радула. К. Cadlina sp. 5, центральные и внутренние латеральные Зубы. L. Cadlina sp. 5, центральные Зубы. М. Cadlina sp. 5, внешние латеральные Зубы. N. Cadlina sp. 5, радула на одонтофоре. О. Cadlina sp. 5, лабиальнаЯ кутикула. P. Cadlina sp. 5, Элементы лабиальной кутикулы. Масштабные линейки: A, N, O = 100 мкм; B, E, M = 50 мкм; C, F, I, L = 10 мкм; D, G, H, J = 200 мкм; К, Р = 20 мкм.
FIG. 8 in Fifty shades of white: morphological and molecular diversity of the Cadlina laevis species complex (Gastropoda: Nudibranchia) in the North-West Pacific
FIG. 8. Buccal armature of Cadlina sp. 7 (MIMB47981, Sea of Japan) and Cadlina sp. 4 (MIMB47978, Sea of Japan) (SEM). А. Cadlina sp. 7, radula. B. Cadlina sp. 7, anterior radular portion, rachidian and inner lateral teeth. C. Cadlina sp. 7, outer lateral teeth. D. Cadlina sp. 7, rachidian and innermost lateral teeth. E. Cadlina sp. 4, radula. F. Cadlina sp. 4, anterior radular portion, rachidian and inner lateral teeth. G. Cadlina sp. 4, rachidian and innoermost lateral teeth. H. Cadlina sp. 4, outer lateral teeth. I. Cadlina sp. 4, labial cuticle rodlets. Scale bars: A = 300 µm; B, F = 100 µm; C = 30 µm; D = 10 µm; E = 400 µm; G, I = 20 µm; H = 50 µm. РИС. 8. Буккальное вооруЖение Cadlina sp. 7 (MIMB47981, Японское море) и Cadlina sp. 4 (MIMB47978, Японское море) (СЭМ). А. Cadlina sp. 7, радула. B. Cadlina sp. 7, переднЯЯ часть радулы, центральные и внутренние латеральные Зубы. C. Cadlina sp. 7, наруЖные латеральные Зубы. D. Cadlina sp. 7, центральные и внутренние латеральные Зубы. Е. Cadlina sp. 4, радула. F. Cadlina sp. 4, переднЯЯ часть радулы, центральные и внутренние латеральные Зубы. G. Cadlina sp. 4, переднЯЯ часть радулы, центральные и внутренние латеральные Зубы. H. Cadlina sp. 4, внешние латеральные Зубы. I. Cadlina sp. 4, Элементы лабиальной кутикулы. Масштабные линейки: A = 300 мкм; B, F = 100 мкм; С = 30 мкм; D = 10 мкм; Е = 400 мкм; G, I = 20 мкм; Н = 50 мкм.
FIG. 7 in Fifty shades of white: morphological and molecular diversity of the Cadlina laevis species complex (Gastropoda: Nudibranchia) in the North-West Pacific
FIG. 7. Buccal armature of Cadlina sp. 3 from the Sea of Japan (SEM). A. MIMB47975, radula. B. MIMB47975, anterior radular portion, rachidian and inner lateral teeth. C. MIMB47975, anterior radular portion, outer lateral teeth. D. MIMB47976, radula. E. MIMB47976, anterior radular portion, rachidian and inner lateral teeth. F. MIMB47976, anterior radular portion, outer lateral teeth. G. MIMB47976, odontophore with radula. H. MIMB47976, labial cuticle. I. MIMB47976, labial cuticle rodlets. J. MIMB47973, anterior radular portion, rachidian and inner lateral teeth. K. MIMB47973, anterior radular portion, outer lateral teeth. L. MIMB47973, labial cuticle rodlets. Scale bars: A, D, H = 500 µm; B, C, F, J = 50 µm; E = 100 µm; G = 200 µm; I, L = 10 µm; K = 20 µm. РИС. 7. Буккальное вооруЖение Cadlina sp. 3 иЗ Японского морЯ (SEM). А. MIMB47975, радула. B. MIMB47975, переднЯЯ часть радулы, центральные и внутренние латеральные Зубы. С. MIMB47975, переднЯЯ часть радулы, внешние латеральные Зубы. D. MIMB47976, радула. Е. MIMB47976, переднЯЯ часть радулы, центральные и внутренние латеральные Зубы. F. MIMB47976, переднЯЯ часть радулы, внешние латеральные Зубы. G. MIMB47976, одонтофор с радулой. Н. MIMB47976, лабиальнаЯ кутикула. I. MIMB47976, Элементы лабиальной кутикулы. J. MIMB47973, переднЯЯ часть радулы, центральные и внутренние латеральные Зубы. К. MIMB47973, переднЯЯ часть радулы, внешние латеральные Зубы. L. MIMB47973, Элементы лабиальной кутикулы. Масштабные линейки: A, D, H = 500 мкм; B, C, F, J = 50 мкм; Е = 100 мкм; G = 200 мкм; I, L = 10 мкм; К = 20 мкм.
FIG. 6 in Fifty shades of white: morphological and molecular diversity of the Cadlina laevis species complex (Gastropoda: Nudibranchia) in the North-West Pacific
FIG. 6. Buccal armature of Cadlina sp. 1 (MIMB47971, Urup Is., Sea of Okhotsk) and Cadlina sp. 2 (MIMB42230, Iturup Is., Sea of Okhotsk) (SEM). A. Cadlina sp. 1, radula. B. Cadlina sp. 1, anterior radular portion, rachidian and lateral teeth. C. Cadlina sp. 1, rachidian and innermost lateral teeth. D. Cadlina sp. 1, outer lateral teeth. E. Cadlina sp. 1, outer lateral teeth. F. Cadlina sp. 1, labial cuticle rodlets. G. Cadlina sp. 2, anterior radular portion, rachidian and inner lateral teeth. H. Cadlina sp. 2, outer lateral teeth. I. Cadlina sp. 2, labial cuticle rodlets. Scale bars: A = 500 µm; B = 300 µm; C = 50 µm; D, E = 100 µm; F = 20 µm; G, H = 30 µm; I = 10 µm. РИС. 6. Буккальное вооруЖение Cadlina sp. 1 (MIMB47971, о. Уруп, Охотское море) и Cadlina sp. 2 (MIMB42230, о. Итуруп, Охотское море) (СЭМ). А. Cadlina sp. 1, радула. B. Cadlina sp. 1, переднЯЯ часть радулы, центральные и внутренние латеральные Зубы. C. Cadlina sp. 1, центральные и внутренние латеральные Зубы. D. Cadlina sp. 1, внешние латеральные Зубы. Е. Cadlina sp. 1, внешние латеральные Зубы. F. Cadlina sp. 1, Элементы лабиальной кутикулы. G. Cadlina sp. 2, переднЯЯ часть радулы, центральные и внутренние латеральные Зубы. H. Cadlina sp. 2, внешние латеральные Зубы. I. Cadlina sp. 2, Элементы лабиальной кутикулы. Масштабные линейки: A = 500 мкм; B = 300 мкм; С = 50 мкм; D, Е = 100 мкм; F = 20 мкм; G, Н = 30 мкм; I = 10 мкм.
FIG. 5 in Fifty shades of white: morphological and molecular diversity of the Cadlina laevis species complex (Gastropoda: Nudibranchia) in the North-West Pacific
FIG. 5. Buccal armature of Cadlina laevis s.str., specimens from the White Sea (SEM). A. MIMB47939, radula. B. MIMB47939, anterior radular portion, rachidian and inner lateral teeth. C. MIMB47939, same as B, enlarged. D. MIMB47939, anterior radular portion, outer lateral teeth. E. MIMB47939, odontophore with radula. F. MIMB47939, labial cuticle. G. MIMB47939, labial cuticle rodlets. H. MIMB47963, radula. I. MIMB47963, middle radular portion, rachidian and inner lateral teeth. K. MIMB47963, middle radular portion, rachidian and innermost laterals. L. MIMB47963, outer lateral teeth. M. MIMB47963, odontophore with radula. N. MIMB47963, labial cuticle. O. MIMB47963, labial cuticle rodlets. Scale bars: A, E, H = 200 µm; B, D, I = 50 µm; C, K, L, N = 20 µm; F, M = 100 µm; G = 10 µm; O = 5 µm. РИС. 5. Буккальное вооруЖение Cadlina laevis s.str., особи иЗ Белого морЯ (СЭМ). A. MIMB47939, радула. B. MIMB47939, переднЯЯ часть радулы, центральные и внутренние латеральные Зубы. C. MIMB47939, то Же, что B, увеличенное. D. MIMB47939, переднЯЯ часть радулы, внешние латеральные Зубы. E. MIMB47939, одонтофор с радулой. F. MIMB47939, лабиальнаЯ кутикула. G. MIMB47939, родлеты лабиальной кутикулы. H. MIMB47963, радула. I. MIMB47963, среднЯЯ часть радулы, центральные и внутренние латеральные Зубы. K. MIMB47963, среднЯЯ часть радулы, центральные и внутренние латеральные Зубы. L. MIMB47963, наруЖные латеральные Зубы. М. MIMB47963, одонтофор с радулой. N. MIMB47963, лабиальнаЯ кутикула. O. MIMB47963, родлеты лабиальной кутикулы. Масштабные линейки: A, E, H = 200 мкм; B, D, I = 50 мкм; С, К, L, N = 20 мкм; F, М = 100 мкм; G = 10 мкм; О = 5 мкм.
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Allen Brain Atlas
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DANDI Archive for NWB datasets
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International Brain Laboratory public data
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OpenNeuro
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