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Eco-Friendly Suppression of Xanthomonas axonopodis pv. punicae: The Role of Lactobacillus helveticus PMP-6 in Pomegranate Disease Management
Pravin Vasantrao Deshmukh,
Prakash Ramrao Thorat,
Sopan Ganpatrao Wagh,
Bhausaheb D. Pawar,
Bhausaheb Dyanoba Pawar
Posted: 12 December 2024
Generalised Additive Model based Regional Flood Frequency Analysis: Parameter Regression Technique Using Generalised Extreme Value Distribution
Laura Rima,
Khaled Haddad,
Ataur Rahman
Posted: 12 December 2024
Experimental Setup and Machine Learning-Based Prediction Model for Electro Cyclone Filter Efficiency: Filtering of Ship Particulate Matter Emission
Aleksandr Šabanovič,
Jonas Matijošius,
Dragan Marinković,
Aleksandras Chlebnikovas,
Donatas Gurauskis,
Johannes H. Gutheil,
Artūras Kilikevičius
Posted: 12 December 2024
omplementary Inoculation of Emerged Soybean with the Growth-Promoting Bacteria Azospirillum, Pseudomonas, Priestia and Bacillus
Robélio Leandro Marchão,
Gustavo Cassiano da Silva,
Solange Rocha Monteiro de Andrade,
Fábio Bueno dos Reis Junior,
Márcio Pereira de Barros Júnior,
Richard Hemanwel Haphonsso,
Arminda Moreira de Carvalho
Posted: 12 December 2024
Chemo-Mineralogical Changes of Six European Monumental Stones Caused by Cyclic Isothermal Treatment at 600 °C
Matea Urbanek,
Karin Wriessnig,
Werner Artner,
Farkas Pintér,
Franz Ottner
Posted: 12 December 2024
Calibration and Validation of the SWAT Model for Upper Bernam River Basin in Malaysia
Muazu Dantala Zakari,
Md Kamal Rowshon,
Norulhuda Binti Mohamed Ramli,
Balqis Mohamed Rehan,
Mohd Syazwan Faisal Bin Mohd,
Franklin Aondoaver Kondum
Enhancing sustainable agricultural practices and water resources management calls for this study, which focuses on calibrating and validating the SWAT model using data from CMIP6. The SWAT model was validated using Bernam streamflow data from 1985-2022, divided into three categories: category 1 (10 years calibration- and 5 years validation), category 2 (15 years calibration- and 10 years validation), and category 3. The SWAT model performed "GOOD" in the Bernam watershed, as indicated by statistical analysis during calibration and validation phases, utilizing statistical indices. The results for the p-factor, r-factor, R2, NSE, PBIAS, and KGE were 0.82, 0.88, 0.72, 0.70, -1.1%, and 0.85 during the calibration period and 0.8, 1.04, 0.75, 0.65, -6.6%, and 0.79 during the validation period. The result of the simulation after adjusting the SWAT model parameters with calibrated best-fit values indicated that the inflow (rainfall) and the outflow (water yield + ET) are 2,873.36mm and 2,592.78mm respectively, with difference of 9.8% for the period of 1991-2005 while 2,921.98 mm and 2,586.07 mm for the inflow and outflow, during 2006-2020 period with difference of 11.5%. The SWAT model effectively predicts agro-hydrological processes, aiding decision-makers in UBRB's agricultural water management and guiding sustainable agriculture through advanced climate projections.
Enhancing sustainable agricultural practices and water resources management calls for this study, which focuses on calibrating and validating the SWAT model using data from CMIP6. The SWAT model was validated using Bernam streamflow data from 1985-2022, divided into three categories: category 1 (10 years calibration- and 5 years validation), category 2 (15 years calibration- and 10 years validation), and category 3. The SWAT model performed "GOOD" in the Bernam watershed, as indicated by statistical analysis during calibration and validation phases, utilizing statistical indices. The results for the p-factor, r-factor, R2, NSE, PBIAS, and KGE were 0.82, 0.88, 0.72, 0.70, -1.1%, and 0.85 during the calibration period and 0.8, 1.04, 0.75, 0.65, -6.6%, and 0.79 during the validation period. The result of the simulation after adjusting the SWAT model parameters with calibrated best-fit values indicated that the inflow (rainfall) and the outflow (water yield + ET) are 2,873.36mm and 2,592.78mm respectively, with difference of 9.8% for the period of 1991-2005 while 2,921.98 mm and 2,586.07 mm for the inflow and outflow, during 2006-2020 period with difference of 11.5%. The SWAT model effectively predicts agro-hydrological processes, aiding decision-makers in UBRB's agricultural water management and guiding sustainable agriculture through advanced climate projections.
Posted: 12 December 2024
Methods to Establish Reference Models for Ecological Restoration—Case Study from Colorado National Monument, USA
Patrick J. Comer,
Gregory E. Eckert,
George D. Gann
Restoration practitioners specify targets for what the ecosystem will look like to reach recovery goals. Targets may be influenced by the level of degradation, surrounding landscape conditions, societal choice, and a changing and uncertain climate regime. The Society for Ecological Restoration’s International Principles and Standards for the Practice of Ecological Restoration recommends that targets be informed by reference models of site conditions that include biotic composition, environmental setting, and dynamic processes—had anthropogenic degradation not occurred—while accounting for anticipated change. Models optimally reflect a variety of information sources and are based where possible on multiple reference sites of similar native ecological conditions. Using a project site from Colorado National Monument, we illustrate a stepwise process for compiling and synthesizing map, text, and tabular information from reference materials and sites. Reference materials include multiple ecosystem classifications and site inventories to describe composition, structure, and dynamics of the target ecosystems. An ecological integrity framework aids in identifying key ecological attributes and indicators for site measurement. Climate change vulnerability assessment specifies risks to anticipate, while adaptation frameworks point to appropriate strategies. By systematically utilizing existing frameworks and available data, practitioners can streamline the establishment of reference models for ecological restoration.
Restoration practitioners specify targets for what the ecosystem will look like to reach recovery goals. Targets may be influenced by the level of degradation, surrounding landscape conditions, societal choice, and a changing and uncertain climate regime. The Society for Ecological Restoration’s International Principles and Standards for the Practice of Ecological Restoration recommends that targets be informed by reference models of site conditions that include biotic composition, environmental setting, and dynamic processes—had anthropogenic degradation not occurred—while accounting for anticipated change. Models optimally reflect a variety of information sources and are based where possible on multiple reference sites of similar native ecological conditions. Using a project site from Colorado National Monument, we illustrate a stepwise process for compiling and synthesizing map, text, and tabular information from reference materials and sites. Reference materials include multiple ecosystem classifications and site inventories to describe composition, structure, and dynamics of the target ecosystems. An ecological integrity framework aids in identifying key ecological attributes and indicators for site measurement. Climate change vulnerability assessment specifies risks to anticipate, while adaptation frameworks point to appropriate strategies. By systematically utilizing existing frameworks and available data, practitioners can streamline the establishment of reference models for ecological restoration.
Posted: 12 December 2024
WindRAD Scatterometer Quality Control in Rain
Zhen Li,
Anton Verhoef,
Ad Stoffelen
Rain backscatter corrupts Ku-band scatterometer wind retrieval by mixing with the signatures of the backscatter measurements () on the sea surface. The measurements are sensitive to rain clouds due to the short wavelength, and the rain-contaminated measurements in a WVC (Wind Vector Cell) deviate from the measurements that are simulated using the wind GMF (Geophysical Model Function). Therefore, QC (Quality Control) is essential to guarantee the retrieved winds' quality and consistency. The normalized MLE (Maximum Likelihood Estimator) residual () is a QC indicator representing the distance between the measurements and the wind GMF; it works locally for one WVC. is another QC indicator. It is the speed component of the observation cost function, which is sensitive to spatial inconsistencies in the wind field. is a combined indicator, and it takes both local information () and spatial consistency () into account. This paper focuses on WindRAD on the FY-3E (Fengyun-3E) satellite, a dual-frequency (C and Ku band) rotating-fan-beam scatterometer. The and have been established and thoroughly investigated for Ku-band-only and combined C&Ku wind retrieval. A polynomial fit is applied to select the optimal threshold. The C-band measurements are hardly influenced by rain, so the Ku-based is proposed for the C&Ku wind retrieval instead of the total from both C and Ku bands. In conclusion, the gives the optimal QC result for the Ku-band-only and C&Ku wind retrieval. Adding the C-band into the retrieval suppresses the rain effect; therefore, a promising QC skill can be achieved with fewer rejected winds.
Rain backscatter corrupts Ku-band scatterometer wind retrieval by mixing with the signatures of the backscatter measurements () on the sea surface. The measurements are sensitive to rain clouds due to the short wavelength, and the rain-contaminated measurements in a WVC (Wind Vector Cell) deviate from the measurements that are simulated using the wind GMF (Geophysical Model Function). Therefore, QC (Quality Control) is essential to guarantee the retrieved winds' quality and consistency. The normalized MLE (Maximum Likelihood Estimator) residual () is a QC indicator representing the distance between the measurements and the wind GMF; it works locally for one WVC. is another QC indicator. It is the speed component of the observation cost function, which is sensitive to spatial inconsistencies in the wind field. is a combined indicator, and it takes both local information () and spatial consistency () into account. This paper focuses on WindRAD on the FY-3E (Fengyun-3E) satellite, a dual-frequency (C and Ku band) rotating-fan-beam scatterometer. The and have been established and thoroughly investigated for Ku-band-only and combined C&Ku wind retrieval. A polynomial fit is applied to select the optimal threshold. The C-band measurements are hardly influenced by rain, so the Ku-based is proposed for the C&Ku wind retrieval instead of the total from both C and Ku bands. In conclusion, the gives the optimal QC result for the Ku-band-only and C&Ku wind retrieval. Adding the C-band into the retrieval suppresses the rain effect; therefore, a promising QC skill can be achieved with fewer rejected winds.
Posted: 12 December 2024
Significance of Time Value When Comparing Alternatives for Building Decarbonization
Kate Chilton,
Jay Arehart,
Hal Hinkle
Posted: 11 December 2024
Major And Minor Causes Of Geophagy-Lithophagy In Animals And Humans
Alexander M Panichev,
Kirill S Golokhvast
Posted: 11 December 2024
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