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A spatial autocorrelation analysis of environmental factors related to Dengue using Moran's I spatial statistics: A study from Nepal 2020-2023
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Table 4 in Temperate grassy wetlands of South Africa: Description, classification and explanatory environmental factors
<p><b>Table 4</b> Description of vegetation types of temperate grassy wetlands.</p><table><tbody><tr><th>No.</th><th>Wetland vegetation type</th><th>No. comm.</th><th>Dominant species</th><th>Vegetation structure</th><th>Environmental conditions</th><th>Distribution</th><th>Comments</th><th>Species diversity</th></tr></tbody><tbody><tr><th>1</th><td>Waterbiesie</td><td>2</td><td><i>Eleocharis dregeana, Leersia</i></td><td>Dense, medium tall sedges or</td><td>Mostly pans, gleyed clay soils,</td><td>Inland parts of Eastern South</td><td><i>Leersia hexandra</i> is the most common</td><td>Median 6</td></tr><tr><th></th><td>wetlands</td><td></td><td><i>dregeana</i></td><td>grasses (20–50 cm tall)</td><td>seasonally or permanently wet</td><td>Africa</td><td>wetland grass in South Africa</td><td>(1–23)</td></tr><tr><th>2</th><td>Pond sedge wetlands</td><td>1</td><td><i>Carex acutiformis</i></td><td>Dense medium tall sedges (30–80</td><td>Mostly valley bottom wetlands, on</td><td>Inland parts of Eastern South</td><td>The species <i>Carex acutiformis</i> is</td><td>Median 4</td></tr><tr><th></th><td></td><td></td><td></td><td>cm tall)</td><td>clay or peat, permanently wet</td><td>Africa, mostly around the</td><td>widely distributed and it is not clear</td><td>(1–18)</td></tr><tr><th></th><td></td><td></td><td></td><td></td><td></td><td>escarpment</td><td>whether it is indigenous to South</td><td></td></tr><tr><th></th><td></td><td></td><td></td><td></td><td></td><td></td><td>Africa</td><td></td></tr><tr><th>3</th><td>Grassy everlasting</td><td>1</td><td><i>Aristida junciformis,</i></td><td>Dense short grassland (20–50 cm tall)</td><td>Seasonally or temporarily wet</td><td>Inland parts of Eastern South</td><td>Conspicuous because of the presence</td><td>Median 13</td></tr><tr><th></th><td>wetlands</td><td></td><td><i>Helichrysum aureonitens</i></td><td></td><td>grasslands, mostly on loam soils</td><td>Africa, most common around the</td><td>of the everlasting <i>Helichrysum</i></td><td>(5–24)</td></tr><tr><th></th><td></td><td></td><td></td><td></td><td></td><td>Drakensberg</td><td><i>aureonitens</i></td><td></td></tr><tr><th>4</th><td>Highveld mixed</td><td>6</td><td><i>Cyperus denudatus,</i></td><td>Dense medium tall to tall sedge or</td><td>Various habitats, mostly in valley</td><td>Widespread in Eastern South</td><td>Few communities are dominated by</td><td>Median 8</td></tr><tr><th></th><td>sedge wetlands</td><td></td><td><i>Schoenoplectus brachyceras,</i></td><td>grassland (20–120 cm tall)</td><td>bottom wetlands and floodplains, on</td><td>Africa, but also in the Cape</td><td>grasses, but the wetter communities</td><td>(1–22)</td></tr><tr><th></th><td></td><td></td><td><i>Juncus effusus</i></td><td></td><td>clay or loam soils of different wetness</td><td></td><td>by sedges and rushes</td><td></td></tr><tr><th>5</th><td>Eragrostis</td><td>1</td><td><i>Eragrostis planiculmis</i></td><td>Dense tall grassland (80–120 cm)</td><td>Temporarily to seasonally wet clay soils</td><td>Inland parts of Eastern South</td><td></td><td>Median 9</td></tr><tr><th></th><td>planiculmis wetlands</td><td></td><td></td><td></td><td></td><td>Africa</td><td></td><td>(3–19)</td></tr><tr><th>6</th><td>Chichi mixed</td><td>2</td><td><i>Arundinella nepalensis,</i></td><td>Dense tall grassland (80–120 cm) or</td><td>Temporarily to seasonally wet loam</td><td>Inland parts of Eastern South</td><td>The bush ‘Chichi’ or ‘Ouhout’ becomes</td><td>Median 11</td></tr><tr><th></th><td>wetlands</td><td></td><td><i>Leucosidea sericea</i></td><td>short grassland with shrubs up to 3 m.</td><td>soils, mostly in mountainous terrain</td><td>Africa, most common around the</td><td>dominant in disturbed grasslands, but</td><td>(3–24)</td></tr><tr><th></th><td></td><td></td><td></td><td></td><td></td><td>Drakensberg</td><td>also in floodplains and seepages</td><td></td></tr><tr><th>7</th><td>Rooivleigrass</td><td>3</td><td><i>Hemarthria altissima,</i></td><td>Open to dense, medium tall grassland</td><td>Mostly around the edge of pans or</td><td>Inland parts of eastern South</td><td></td><td>Median 9</td></tr><tr><th></th><td>wetlands</td><td></td><td><i>Cyperus marginatus,</i></td><td>or sedgeland (30–60 cm)</td><td>valley bottom wetlands, on temporarily</td><td>Africa, extending into the Western</td><td></td><td>(2–34)</td></tr><tr><th></th><td></td><td></td><td><i>Paspalum dilatatum</i></td><td></td><td>to seasonally wet loam soils</td><td>Free State</td><td></td><td></td></tr><tr><th>8</th><td>Red grass wetlands</td><td>1</td><td><i>Themeda triandra</i></td><td>Dense short grassland (20–50 cm tall)</td><td>Temporarily wet grassland areas</td><td>Widespread across the Highveld</td><td>The grass <i>Themeda triandra</i></td><td>Median 11</td></tr><tr><th></th><td></td><td></td><td></td><td></td><td></td><td>and around the Drakensberg</td><td>represents the most dominant grass</td><td>(3–26)</td></tr><tr><th></th><td></td><td></td><td></td><td></td><td></td><td></td><td>species in the upland areas of the</td><td></td></tr><tr><th></th><td></td><td></td><td></td><td></td><td></td><td></td><td>Highveld region, and it can deal</td><td></td></tr><tr><th></th><td></td><td></td><td></td><td></td><td></td><td></td><td>reasonably well with inundation</td><td></td></tr><tr><th>9</th><td>Cyperus fastigiatus</td><td>1</td><td><i>Cyperus fastigiatus</i></td><td>Dense tall sedgeland (100–180 cm</td><td>Permanently wet areas in valley bottom</td><td>Throughout the country, including</td><td>Different forms of the species occur,</td><td>Median 6</td></tr><tr><th></th><td>wetlands</td><td></td><td></td><td>tall)</td><td>wetlands, either on clay or peat</td><td>the Cape and tropical areas, but</td><td>especially in the tropical areas</td><td>(1–16)</td></tr><tr><th></th><td></td><td></td><td></td><td></td><td></td><td>absent from the drier areas</td><td></td><td></td></tr><tr><th>10</th><td>Silver spike grass</td><td>4</td><td><i>Imperata cylindrica,</i></td><td>Medium tall to tall mixed</td><td>Temporarily to seasonally wet,</td><td>Mostly in the Northern Highveld,</td><td><i>Imperata cylindrica</i> is commonly</td><td>Median 10</td></tr><tr><th></th><td>wetlands</td><td></td><td><i>Miscanthus junceus</i></td><td>grasslands (50–120 cm)</td><td>mostly sandy areas</td><td>Northern KwaZulu-Natal and in the</td><td>found in disturbed soils, for example</td><td>(2–30)</td></tr><tr><th></th><td></td><td></td><td></td><td></td><td></td><td>Cape</td><td>in road verges</td><td></td></tr><tr><th>11</th><td>Eragrostis plana</td><td>1</td><td><i>Eragrostis plana</i></td><td>Open to dense medium tall</td><td>Temporarily or seasonally wet loam</td><td>Inland parts of Eastern South Africa</td><td>Often an indicator of disturbance</td><td>Median 11</td></tr><tr><th></th><td>wetlands</td><td></td><td></td><td>grassland</td><td>or clay soils</td><td>as well as the Cape</td><td></td><td>(4–27)</td></tr><tr><th>12</th><td>Common bullrush</td><td>1</td><td><i>Typha capensis</i></td><td>Dense tall reedlands</td><td>Seasonally to permanently wet clay or</td><td>Common in Northern South Africa,</td><td>The dominant species occurs often in</td><td>Median 4.5</td></tr><tr><th></th><td>wetlands</td><td></td><td></td><td></td><td>peat soils, often with high nutrient</td><td>Natal and the Cape</td><td>urban wetlands as it can deal very</td><td>(1–18)</td></tr><tr><th></th><td></td><td></td><td></td><td></td><td>loads</td><td></td><td>well with pollution and high nutrient</td><td></td></tr><tr><th></th><td></td><td></td><td></td><td></td><td></td><td></td><td>loads</td><td></td></tr><tr><th>13</th><td>Common reed</td><td>1</td><td><i>Phragmites australis</i></td><td>Open to dense tall reedlands</td><td>Many different habitats, mostly</td><td>Throughout the whole country</td><td>One of the most competitive wetland</td><td>Median 4</td></tr><tr><th></th><td>wetlands</td><td></td><td></td><td></td><td>seasonally to permanently wet, also</td><td></td><td>plants. Benefits from high nutrient</td><td>(1–30)</td></tr><tr><th></th><td></td><td></td><td></td><td></td><td>dealing well with salinity</td><td></td><td>loads and stabilized water levels.</td><td></td></tr></tbody></table>
Fig. 4 in Environmental factors related to entry into and ascent of fish in the experimental ladder located close to Itaipu Dam
Fig. 4. Temporal variability (a) and correlogram of total abundance (b) of fish recorded in the experimental fish ladder (Pool A = 10 m, Pool B = 27 m) located near Itaipu Dam.
Environmental factors, habitats and density of rare and endangered plants
<p>This dataset contains data from the list of the National Key Protected Wild Plants (the first and second batches) officially approved by the State Council, 1898 plants were recorded in the information system of the Chinese Rare and Endangered Plants. The dataset includes: name of species (Latin Name), Place (counties in China), Latitude and Longitude (coordinates<span><span><span><span><span><span><span> of the Place), MAP (Mean annual precipitation), MAT (Mean annual temperature) and MAH (Mean annual humidity), Altitude (Vertical distribution of habit of the rare and endangered plants), Habit (Habit type of the rare and endangered plants), Species density (number of plant species/ log (area of a county)). </span></span></span></span></span></span></span></p> <p>In the study, we collected information on climate, altitude, habitat, and distribution of rare and endangered plants in China, to determine their habitat characteristics, geographical distribution, and the relationships between environmental factors and species density. We found that rare and endangered plants tend to distribute in warm, humid, and forested habitats. Mountains, rather than plains, hills, wind-accumulated landforms, tablelands, lakes, and glaciers, can provide mesophytic and less-disturbed refuges for rare and endangered plants. In particular, medium and medium high-altitude mountains located in monsoon-dominated regions with high precipitation, temperature, and humidity provide diversified habitats for species of rare and endangered plants with high density.</p>
Plant and soil microbial diversity and related spatial and environmental factors in the grasslands of northern China
<p>Plant and soil microbial diversity and related spatial and environmental factors in the grasslands of northern China from 2018 and 2019. The data included 54 and 27 sites in 2018 and 2019 respectively. The data table contains two sheets, one for 2018 and the other for 2019. Spatial factors include longitude and latitude; climatic factors include mean annual temperature, mean annual precipitation, temperature seasonality, precipitation seasonality, potential evapotranspiration, and aridity index; soil factors include soil bulk density, soil moisture, soil pH, soil organic carbon, soil clay content, soil silt content, soil sand content, soil total carbon, soil total nitrogen, and soil C:N ratio; plant functional diversity include functional richness (FRic), functional evenness (FEve), functional divergence (FDiv), functional dispersion (FDis), Rao's quadratic entropy (RaoQ); community-weighted mean (CWM) traits include specific leaf area (SLA), leaf dry matter content (LDMC), leaf nitrogen content (leafN),ratio of leaf carbon to nitrogen (leaf C:N), and stem density; soil microbial diversity include bacterial diversity and fungal diversity; fungal functional guilds include pathotrophic fungi, saprotrophic fungi, arbuscular mycorrhizal fungi, and ectomycorrhizal fungi; bacterial functional guilds include aerobic chemoheterotrophy, predatory or exoparasitic, cellulolysis, aerobic nitrite oxidation, sulfur respiration, nitrate reduction, ureolysis, aromatic compound degradation, intracellular parasites, fermentation, and methanotrophy in the data sheet of 2018. </p> <p><br> Soil microbial diversity include bacterial diversity and fungal diversity; fungal functional guilds include pathotrophic fungi, saprotrophic fungi, arbuscular mycorrhizal fungi, and ectomycorrhizal fungi; bacterial functional guilds include aerobic chemoheterotrophy, predatory or exoparasitic, cellulolysis, aerobic nitrite oxidation, sulfur respiration, nitrate reduction, ureolysis, aromatic compound degradation, intracellular parasites, fermentation, and methanotrophy in the data sheet of 2019.</p>
Figure 1 in Sex inversion in cultivated mussels Mytilus galloprovincialis Lam. (Crimea, Black Sea) under influence of external environmental factors
Figure 1. Sex distribution after six-month exposure of females of the mussel M. galloprovincialis in 2016 in water of (A) the mussel-and-oyster farm area (81 specimens survived mussels) and (B) polluted area (31 specimens survived mussels).
Fig. 5 in Quantitative variations of usnic acid and selected elements in terricolous lichen Cladonia mitis Sandst., with respect to different environmental factors - A chemometric approach
Fig. 5. Map of the sampling localities (N1 – P7) along the transect.
Data from: Seasonal and daily xylem radius variations in Scots pine are closely linked to environmental factors affecting transpiration
<p>The data file (<strong>Dendrometer_data_Pisy.xlsx</strong>) contains environmental records and dendrometer data, i.e., raw data as well as calculated mean daily radial variations of the xylem and inner bark, detrended radial variations of the xylem and inner bark, and daily xylem amplitudes.</p> <p><strong>Data are documented in the following article</strong>:</p> <p>Oberhuber W, A Gruber, G Wieser (2023) Seasonal and daily xylem radius variations in Scots pine are closely linked to environmental factors affecting transpiration<strong>. </strong>Biology, 12, 1251; doi: 10.3390/ biology12091251</p> <p><strong>Summary</strong></p> <p>Diurnal and seasonal radius variations of xylem and inner bark of mature Scots pine trees (<em>Pinus sylvestris</em>; stem diameter 27±2 cm) were determined at a drought prone inner alpine site (<em>c</em>. 750 m asl; Tyrol, Austria). Point dendrometers were mounted on xylem and on living phloem (i.e., inner bark) of four trees, and xylem radius variations (XRV) were continuously recorded throughout three growing seasons (April 2019–October 2021) and related to environmental factors including air temperature (T), vapour pressure deficit of the air (VPD), relative air humidity (RH), solar radiation (SR), precipitation (P) and soil water content (SWC). While inner bark width increased due to radial stem growth (<em>c</em>. 500 µm per year), radial xylem width consistently decreased by <em>c</em>. 50 µm during the growing seasons. Results of our study revealed that daily and seasonal radial variations of the xylem and inner bark were closely linked, indicating intensive water exchange between these tissues. Comparison of XRV with environmental variables affecting transpiration revealed a close coupling of XRV to VPD, T and SR, pointing to a strong dependence of stem water status on changes in atmospheric conditions. Because VPD increases exponentially with the increase in temperature and thus causes the water content in the stem to decrease especially under drought, tree growth and mortality will be increasingly affected by climate warming.</p> <p> </p>
Genomics, Environmental Factors and Social Determinants of Cardiovascular Disease in African Americans Study (GENE-FORECAST): Sodium Intervention Trial (SIT)
ClinicalTrials.gov study NCT04717336. IPD Sharing: NO. Countries: 1. Publications: 0.
Environmental and Behavioral Risk Factors for Childhood Drowning
ClinicalTrials.gov study NCT00341289. IPD Sharing: Not stated. Countries: 1. Publications: 3.
Does Environmental Factors Affect Accuracy in Pre-hospital Non-invasive Temperature Measurement?
ClinicalTrials.gov study NCT02274597. IPD Sharing: Not stated. Countries: 0. Publications: 1.
Evaluation of the Role of Aflatoxin as an Environmental Risk Factor Attributable to Liver Cancer in Nile Delta
ClinicalTrials.gov study NCT02461966. IPD Sharing: NO. Countries: 1. Publications: 0.
The Effect of Environmental Factors on Gastric Cancer Based on Macrogenome
ClinicalTrials.gov study NCT06854146. IPD Sharing: NO. Countries: 1. Publications: 0.
The Effects of Environmental Factors on the Macro-genome and Metabolism of Obese Patients.
ClinicalTrials.gov study NCT06673433. IPD Sharing: NO. Countries: 1. Publications: 0.
Influence of Social and Environmental Factors on Women's Reproductive Function in a Maya Community of Guatemala
ClinicalTrials.gov study NCT00340782. IPD Sharing: Not stated. Countries: 1. Publications: 1.
the Effect of Environmental Factors on Colorectal Cancer Based on Macrogenomes
ClinicalTrials.gov study NCT06852495. IPD Sharing: NO. Countries: 1. Publications: 0.
Data from: Linking genetic and environmental factors in amphibian disease risk
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Data from: Metabarcoding reveals environmental factors influencing spatio-temporal variation in pelagic micro-eukaryotes
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Data from: Do prevailing environmental factors influence human preferences for facial morphology?
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Databank floristics, phytogeography and environmental factors of the Brazilian Middle North Savannas
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Allen Brain Atlas
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Annotated Behaviour and Observability Dataset (ABODe)
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OpenNeuro
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