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51 results for “Terracing”
Biomass from six vegetation types along a toposequence on a floodplain terrace of the Sagavanirktok River, Alaswka,1988, Arctic LTER.
Biomass was harvested from six vegetation types along a toposequence on a floodplain terrace of the Sagavanirktok River in the northern foothills of the Brooks Range , Alaska (68degrees 46' N, 148 degrees 51' W 50m). The vegetation sites are; upland tussock tundra, "hilltop heath", a "hillslope shrub-lupine", a "footslope Equisetum", a wet sedge tundra, and a "riverside willow".
Surveyed terrace profiles and terrace radiocarbon ages, western Jumgal basin, Tien Shan, Kyrgyz Republic
<p>This archive contains survey data and radiocarbon ages from deformed terraces in the western Jumgal basin, Kyrgyz Republic. These data support analysis by Coddington and Burgette (2020) to be published in <em>Tectonics</em>: “Fold kinematics and fault slip rates from progressively deformed terraces: Implications for structural evolution of basins in the Kyrgyz Tien Shan” </p>
DEMs and orthophotos of a kame terrace, a proglacial lake and a proglacial valley close to the Mittivakkat glacier in East Greenland.
<p>The raw data was acquired using a Platinum MavikPro drone. The images were imported in Agisoft Metashape and a DEM and orthophoto were created following the workflow for the generation of an orthophoto and DEM (without GCPs) as provided on the Agisoft Metashape Website. The DEM height was corrected using the ArcticDEM and the Pleaides DEM as references. In case of the proglacial lake, the lake surface in the DEM was smoothed to eliminate the artefacts in the water areas, which resulted from the DEM generation based on stereo-imagery. </p>
Terraces survey data of the Danghe Nan Shan
<p>The file of <a href="https://zenodo.org/api/files/1387adfc-fd37-4fd0-b944-17a082c31e40/theodolite-distancemeter%20-NXYZ%28m%29.txt">theodolite-distancemeter -NXYZ(m).txt</a> is digital-recording theodolite-distancemeter survey points collected in 1996 at Site 1. </p> <p>The file of <a href="https://zenodo.org/api/files/1387adfc-fd37-4fd0-b944-17a082c31e40/topo-profile-2020-GPS%20points2022.txt">topo-profile-2020-GPS points2022.txt</a> is the differential global position system survey points collected in 2020 at site 1.</p> <p> </p>
Drinking Fountain Albert Terrace
A drinking fountain on the east side of Primrose Hill at the junction of Albert Terrace and Regent's Park Road, London. Date: 1872 http://www.mdfcta.co.uk/details-f/f125.html 228 photos taken in June 2020 with a Sony a6000 and processed in Reality Capture. Source: Objaverse 1.0 / Sketchfab
Fig. 3 in Terrace springs: habitat haven for macrobenthic fauna in the lower plain of the River Ticino (Lombardy, Northern Italy)
Fig. 3 - Cluster analysis of the macrobenthic community collected in Spring 2.
Fig. 2 in Terrace springs: habitat haven for macrobenthic fauna in the lower plain of the River Ticino (Lombardy, Northern Italy)
Fig. 2 - Cluster analysis of the macrobenthic community collected in Spring 1.
Fig. 1 in Terrace springs: habitat haven for macrobenthic fauna in the lower plain of the River Ticino (Lombardy, Northern Italy)
Fig. 1 - Study area.
Dwelling conversion and energy retrofit modify building anthropogenic heat emission under past and future climates: a case study of London terraced houses
<p>This archive includes the data used (e.g. Time use survey (UK-TUS) data), model files (idf files for running EnergyPlus) and codes for analysis in the paper (<a title="Persistent link using digital object identifier" href="https://doi.org/10.1016/j.enbuild.2024.114668" target="_blank" rel="noreferrer noopener">https://doi.org/10.1016/j.enbuild.2024.114668</a>).</p> <p>Files in this archive should include:</p> <ul> <li>Time use survey data analysis</li> </ul> <p>o Main dataset: TUS_activity.zip</p> <p>o Code: TUS_clustering_code.zip</p> <p>o Output: InternalHeatProfile.zip</p> <ul> <li>Building energy modeling </li> </ul> <p>o Main dataset (run in EnergPlus 9.4): IDFfiles.zip</p> <p>o Output: Eplus_output.zip</p> <ul> <li>PostProcess analysis</li> </ul> <p>o Code: QF_analysis_code.zip</p> <p>o Output: QF_output.zip</p> <p> </p> <p>Note: this version currently only includes the outputs of all processes, the main dataset and code will be updated later.</p>
Data from: Promoting plant diversity and habitat heterogeneity through vineyard terracing
<p><strong><span>Questions</span></strong><span>:</span> <span>Viticulture on steep slopes has shaped landscape and biodiversity in many regions, but insufficient profitability has led to management cessation and shrub encroachment. A solution to maintain cultivation economically viable could be vineyard terracing. We aimed </span><span>to identify the potential of terracing to enhance plant diversity and habitat heterogeneity in vineyards, analyse effects of management intensity on vineyard vegetation, and assess how </span><span>plant communities change after vineyard abandonment.</span></p> <p><span><strong>Location</strong>:</span><span> Wine-growing region of the Upper Middle Rhine Valley in Hesse (50.042342°N, 7.814533°E) and Rhineland-Palatinate (50.119139°N, 7.719275°E), Germany.</span><span> </span></p> <p><span><strong>Methods</strong>:</span><span> We recorded vascular plant species and local vineyard parameters in vertically oriented vineyards with vegetated and tilled open inter-rows, in terraced vineyards with tilled terrace inter-rows and extensively managed embankments and in vineyard fallows in a total of 45 study sites. We used plant species richness, Ellenberg indicator values and Grime's strategy types to describe how traits and ecological requirements respond to distinct vineyard management.</span><span> </span></p> <p><span><strong>Results</strong>:</span><span> Plant species richness and composition were determined by management-derived disturbance intensities. Extensively managed embankments had a distinct plant community, the highest plant species richness, more perennial and indicator species, and lower nitrogen indicator values compared to inter-rows. In contrast, highly disturbed open and terrace inter-rows revealed plant communities associated with annuals and ruderals, but species richness did not differ between terrace inter-rows and embankments. Plant communities of fallows were completely different with lower plant diversity. </span><span> </span></p> <p><span><strong>Conclusions</strong>:</span> <span>Our results highlight the potential of terraced vineyards for plant diversity with nutrient-poor, extensively managed embankments providing conditions that have become rare in modern agricultural systems. A long environmental gradient from terrace inter-rows to embankments created habitat heterogeneity at a narrow space. In contrast, intensive inter-row management in vertically oriented vineyards hampers high plant diversity and abandonment</span><span> fosters the spread of woody species at the expanse of plant diversity.</span></p>
Data from: Promoting plant diversity and habitat heterogeneity through vineyard terracing
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Data from: The impact of river capture on fluvial terraces and bedrock incision
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FIGURE 20. Velatida. A. Remaster palmatus. Stetson Mesa Terrace, 445.4 m. B in New species, occurrence records and observations of predation by deep-sea Asteroidea (Echinodermata) from the North Atlantic by NOAA ship Okeanos Explorer
FIGURE 20. Velatida. A. Remaster palmatus. Stetson Mesa Terrace, 445.4 m. B. Large specimen (30.0 cm total diameter) of Pythonaster atlantidis, NW Florida Escarpment, 1970 m. C and D. Pythonaster atlantidis sponge predation. DeSoto Canyon, 2604 m, showing dorsal and oral views (C&D respectively). E. Feeding on hexactinellid sponge. Jaguey Spur, off Puerto Rico, 2668 m. Feeding.
Data from: Land abandonment and intensification diminish spatial and temporal β-diversity of grassland plants and herbivorous insects within paddy terraces
1. Although traditional land-use and management practices are known to enhance environmental heterogeneity in agricultural lands, loss of heterogeneity resulting from recent land-use changes can lead to spatiotemporal β-diversity losses (biotic homogenization). However, patterns and causes of β-diversity loss, especially at a within-field scale, have remained unexplored. 2. We examined β-diversity declines in plants, butterflies and orthopterans resulting from land abandonment and intensification in semi-natural grasslands on paddy margins at a within-field scale in relation to changes in disturbance frequency and surrounding landscapes by surveying eight abandoned, thirteen traditional and ten intensive paddy terraces. Three indices, the additive partitioning of species richness (βadd) and the turnover (βtu) and nestedness (βne) components of Jaccard dissimilarity of plants and herbivores, were used to evaluate different aspects of β-diversity. We hypothesized that biotic homogenization due to abandonment and intensification would be expressed as low spatiotemporal βadd and βtu, low spatial βne and high temporal βne. 3. The spatial and temporal βadd of plants and herbivores were higher in traditional terraces than in others. Changes in mowing frequency caused direct declines in butterfly βadd and indirectly decreased herbivore βadd through diminished plant βadd in abandoned and intensified terraces. 4. Neighbouring forests increased plant spatial and butterfly temporal βadd and βtu. Abandoned terraces had higher orthopteran spatial and plant temporal βtu than traditional terraces. Mowing frequency generally did not influence spatial and temporal βtu of plants and herbivores. In intensive terraces, temporal βne of plants were higher than in traditional terraces, suggesting dominance by plant species sharing similar phenologies. 4. Synthesis and applications. These results suggest that traditional mowing practices are essential for maintaining plant and herbivore βadd, and consequently, species pools within terraces. The higher spatial or temporal species turnover of plants and orthopterans in abandoned terraces and higher temporal plant nestedness in intensive than in traditional terraces were not due to increases in species pools within terraces. Because within-terrace environmental heterogeneity is thought to remain in abandoned and intensive terraces, we recommend reduction in mowing frequency in intensive terraces and reintroduction of mowing in abandoned terraces for biodiversity restoration.
On following pages: 462. Gray Rice Rat (Eremoryzomys polius); 463. Medium-tailed Rice Rat (Eremoryzomys mesocaudis Brazilian False Rice Rat (Pseudoryzomys simplex); 467. Venezuelan Marsh Rat (Holochilus venezuelae); 468. Amazonian (Holochilus brasiliensis); 471. Crafty Marsh Rat (Holochilus vulpinus); 472. Lagiglia's Marsh Rat (Holochilus lagiglia Rat (Cerradomys maracajuensis); 476. Lindbergh's Rice Rat (Cerradomys scott); 477. Akroa Rice Rat (Cerradomys Goytaca Rice Rat (Cerradomys goytaca); 481. Ucayali Water Rat (Amphinectomys savamis); 482. Trinidad Water Rat Rat (Nectomys apicalis); 485. South American Water Rat (Nectomys rattus); 486. Atlantic Water Rat (Nectomys squamipes), 464. Lund''s Water Rat (Lundomys molitor); 465. Paraguayan Rice Rat (Sooretamys angouya); 466. Marsh Rat (Holochilus sciureus); 469. Chacoan Marsh Rat (Holochilus chacarius); 470. Brazilian Marsh Rat); 473. Langguth's Rice Rat (Cerradomys langguthi); 474. Vivo's Rice Rat (Cerradomys vivoi); 475. Maracaju Rice akroal); 478. Marinho's Rice Rat (Cerradomys marinhus); 479. Terraced Rice Rat (Cerradomys subflavus); 480. (Nectomys palmipes); 483. Magdalena Water Rat (Nectomys magdalenae); 484. Western Amazonian Water ). in Cricetidae
On following pages: 462. Gray Rice Rat (Eremoryzomys polius); 463. Medium-tailed Rice Rat (Eremoryzomys mesocaudis Brazilian False Rice Rat (Pseudoryzomys simplex); 467. Venezuelan Marsh Rat (Holochilus venezuelae); 468. Amazonian (Holochilus brasiliensis); 471. Crafty Marsh Rat (Holochilus vulpinus); 472. Lagiglia's Marsh Rat (Holochilus lagiglia Rat (Cerradomys maracajuensis); 476. Lindbergh's Rice Rat (Cerradomys scott); 477. Akroa Rice Rat (Cerradomys Goytaca Rice Rat (Cerradomys goytaca); 481. Ucayali Water Rat (Amphinectomys savamis); 482. Trinidad Water Rat Rat (Nectomys apicalis); 485. South American Water Rat (Nectomys rattus); 486. Atlantic Water Rat (Nectomys squamipes), 464. Lund''s Water Rat (Lundomys molitor); 465. Paraguayan Rice Rat (Sooretamys angouya); 466. Marsh Rat (Holochilus sciureus); 469. Chacoan Marsh Rat (Holochilus chacarius); 470. Brazilian Marsh Rat); 473. Langguth's Rice Rat (Cerradomys langguthi); 474. Vivo's Rice Rat (Cerradomys vivoi); 475. Maracaju Rice akroal); 478. Marinho's Rice Rat (Cerradomys marinhus); 479. Terraced Rice Rat (Cerradomys subflavus); 480. (Nectomys palmipes); 483. Magdalena Water Rat (Nectomys magdalenae); 484. Western Amazonian Water ).
Distribution. Recorded as living animal from the vicinity of Lake Habbema (3225 m) and an area close to Mt Trikora, WC New Guinea. Late Quaternary subfossils reported (as Hydromys habbema) from Kelangurr Cave and from alluvial terrace of West Baliem River, at 280-2950 m,Papua Province. Tentative record of habbema from a fissure deposit at 3450 m on Mt Jaya requires confirmation. in Muridae
Distribution. Recorded as living animal from the vicinity of Lake Habbema (3225 m) and an area close to Mt Trikora, WC New Guinea. Late Quaternary subfossils reported (as Hydromys habbema) from Kelangurr Cave and from alluvial terrace of West Baliem River, at 280-2950 m,Papua Province. Tentative record of habbema from a fissure deposit at 3450 m on Mt Jaya requires confirmation.
Aztecan Farming Terrace
This is a small diorama based on the farming terraces Source: Objaverse 1.0 / Sketchfab
V&A Dundee Terrace detail
Source: Objaverse 1.0 / Sketchfab
Preservation and destruction of Holocene marine terraces: the effects of episodic versus gradual relative sea level change
<p>Dataset contains RPM source codes, a sample RPM simulation code, and data of the results presented "Preservation and destruction of Holocene marine terraces: the effects of episodic versus gradual relative sea level change"</p>
Data from: Land abandonment and intensification diminish spatial and temporal β-diversity of grassland plants and herbivorous insects within paddy terraces
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OpenNeuro
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