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Search Results (1,709)

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Keywords = reuse potential

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17 pages, 552 KiB  
Review
Innovative Approaches for Sustainable Wastewater Resource Management
by Ayşe Ulusoy, Atılgan Atılgan, Roman Rolbiecki, Barbara Jagosz and Stanisław Rolbiecki
Agriculture 2024, 14(12), 2111; https://doi.org/10.3390/agriculture14122111 (registering DOI) - 22 Nov 2024
Abstract
Sustainable wastewater management is essential for conserving water resources and reducing environmental pollution. Traditional wastewater treatment methods primarily aim to purify water for reuse, yet they often involve high energy consumption, extensive chemical use, and loss of potentially recoverable resources, which pose sustainability [...] Read more.
Sustainable wastewater management is essential for conserving water resources and reducing environmental pollution. Traditional wastewater treatment methods primarily aim to purify water for reuse, yet they often involve high energy consumption, extensive chemical use, and loss of potentially recoverable resources, which pose sustainability challenges. With approximately 2.2 billion people worldwide currently lacking access to clean water—a number projected to exceed 3 billion by 2025—water scarcity has become an urgent issue. Traditional wastewater treatment processes handle around 330 billion cubic meters of water annually; however, they account for 3–4% of global energy consumption and produce 300 million tons of carbon emissions. This situation underscores the need for more sustainable treatment methods. Innovative wastewater treatment technologies have the potential to facilitate the reuse of approximately 50 billion cubic meters of water each year, helping to alleviate water scarcity. Additionally, energy recovery from these processes aims to achieve an annual energy savings of 20 TWh, in contrast to conventional treatment methods. This article examines recent advances in sustainable wastewater management technologies, specifically focusing on biological, physicochemical, and membrane-based processes. It discusses strategies for optimizing these processes to minimize environmental impact. Furthermore, innovative approaches, such as advanced oxidation processes and energy recovery, are explored for their potential to harness energy and recover nutrients from wastewater. The article concludes that implementing innovative strategies in sustainable wastewater management can significantly contribute to water conservation, energy savings, and a reduction in carbon footprint. Full article
(This article belongs to the Section Ecosystem, Environment and Climate Change in Agriculture)
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<p>Particle sizes and purification methods of membrane bioreactor filtrate [<a href="#B10-agriculture-14-02111" class="html-bibr">10</a>,<a href="#B12-agriculture-14-02111" class="html-bibr">12</a>].</p>
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16 pages, 5350 KiB  
Article
Developing a Reclamation Framework to Promote Circularity in Demolition Projects
by Mariah Saad, Rajeev Ruparathna, Nihar Biswas and Edwin Tam
Recycling 2024, 9(6), 114; https://doi.org/10.3390/recycling9060114 (registering DOI) - 22 Nov 2024
Abstract
The construction, demolition, and renovation industries are among the largest contributors to global carbon emissions and waste. With decreased landfill capacities, increased waste diversion targets, resource shortages, and the recognition that material waste is critical to climate change, diverting demolition waste is now [...] Read more.
The construction, demolition, and renovation industries are among the largest contributors to global carbon emissions and waste. With decreased landfill capacities, increased waste diversion targets, resource shortages, and the recognition that material waste is critical to climate change, diverting demolition waste is now a significant priority in waste management. Deconstructing a structure and reusing its building components can significantly reduce the environmental burdens imposed. However, to optimize the reuse of building materials and components for their environmental, societal, and economical benefits, the reclamation procedure must be undertaken in a more rational and robust manner. There are currently gaps in frameworks and tools that involve the assessment of reusable building components in demolition projects. This paper develops a reclamation framework to assess the viability of recovering and reusing building components. The framework first describes a process for conducting a technical audit and uses an assessment tool to suggest a level of deconstruction based on the physical parameters of the building circumstances. The framework complements this initial outcome by then assessing additional comprehensive parameters, such as the cost, the heritage value, and the available timeframe to arrive at a suggested outcome of actions, which can range from complete demolition and basic material recovery to deliberately removing salvageable items. The framework is then applied to an older, detached office building as a conceptual case study for demonstration. The recommended level of deconstruction appears appropriate based on the visual assessment of the structure. The result of this paper promotes the circular economy and supports the United Nations Sustainable Development Goals (UN SDGs) by presenting a notably more insightful and guided approach to capturing deconstruction waste. Full article
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<p>Detached office building assessed.</p>
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<p>Reclamation Audit Assessment Tool template demonstration.</p>
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<p>Reclamation framework stages.</p>
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<p>Reclamation Audit Assessment Tool template.</p>
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24 pages, 8091 KiB  
Article
Influence of Iron Mining Waste Addition as a Sustainable Alternative on the Resilient and Physical Properties of Soils for Pavement Design
by Daniel Corrêa Galhardo, Antônio Carlos Rodrigues Guimarães, Camila Antunes Martins, Murilo Miguel Narciso, Sergio Neves Monteiro and Lisley Madeira Coelho
Sustainability 2024, 16(23), 10211; https://doi.org/10.3390/su162310211 (registering DOI) - 22 Nov 2024
Viewed by 193
Abstract
Mining activities generate large volumes of waste, posing environmental and economic challenges, particularly in Brazil’s Quadrilátero Ferrífero region. This study assesses the potential reuse of iron ore waste from Samarco Mineração S.A. in road pavement layers by blending it with phyllite residual soil [...] Read more.
Mining activities generate large volumes of waste, posing environmental and economic challenges, particularly in Brazil’s Quadrilátero Ferrífero region. This study assesses the potential reuse of iron ore waste from Samarco Mineração S.A. in road pavement layers by blending it with phyllite residual soil (PRS) and lateritic clayey soil (LCS). The addition of 50% waste to PRS led to substantial improvements, increasing the resilient modulus (RM) by up to 130% under medium stress and reducing expansibility from 6.1% to 1%, meeting Brazilian standards for sub-base applications. These enhancements make the PRS-waste blend a viable and sustainable option for reinforcing subgrade and sub-base layers. In contrast, the LCS with 20% waste showed moderate RM improvements under high-stress conditions, while higher waste contents reduced stiffness, indicating that higher dosages may adversely affect performance. This study highlights the potential of inert, non-hazardous mining waste as a safe and efficient solution for pavement applications, promoting the sustainable use of discarded materials. Full article
(This article belongs to the Special Issue Transportation and Infrastructure for Sustainability)
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<p>Visual aspect of the soils and the waste used in this study. (<b>a</b>) PRS. (<b>b</b>) LCS. (<b>c</b>) IMW.</p>
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<p>MCT methodology. (<b>a</b>) MCT equipment. (<b>b</b>) Immersion of the samples immediately after compaction.</p>
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<p>Grain size distribution curves of the aggregates.</p>
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<p>RM test specimen molded inside the tripartite mold dynamic triaxial equipment.</p>
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<p>Grain size distribution curves of the PRS and its mixtures: PRS80/IMW20, PRS60/IMW40, and PRS50/IMW50.</p>
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<p>Grain size distribution curves of the LCS and its mixtures: LCS80/IMW20 and LCS60/IMW40.</p>
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<p>SEM images of the sample fractions at different magnifications: (<b>a</b>) IMW at 300×, (<b>b</b>) PRS at 2500×, and (<b>c</b>) LCS at 500×.</p>
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<p>EDX map of IMW.</p>
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<p>EDX map of PRS.</p>
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<p>EDX map of LCS.</p>
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<p>XRD for the IMW sample, identifying peaks corresponding to goethite, quartz, and hematite.</p>
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<p>XRD for the PRS sample, highlighting the predominant minerals.</p>
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<p>XRD for the LCS sample, indicating the presence of quartz, kaolinite, goethite, and hematite.</p>
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14 pages, 2487 KiB  
Article
Eco-Friendly Synthesis of Thiazole Derivatives Using Recyclable Cross-Linked Chitosan Hydrogel Biocatalyst Under Ultrasonic Irradiation as Anti-Hepatocarcinogenic Agents
by Sobhi M. Gomha, Nahed A. Abd El-Ghany, Manal S. Ebaid, Tariq Z. Abolibda, Magdi E. A. Zaki, Mohammad Alhilal, Suzan Alhilal and Nadia A. Mohamed
Catalysts 2024, 14(12), 840; https://doi.org/10.3390/catal14120840 - 21 Nov 2024
Viewed by 193
Abstract
In the current study, pyromellitimide benzoyl thiourea cross-linked chitosan (PIBTU-CS) hydrogel, was evaluated as a green biocatalyst for the efficient synthesis of novel thiazole derivatives. The PIBTU-CS hydrogel showcased key advantages, such as an expanded surface area and superior thermal stability, establishing it [...] Read more.
In the current study, pyromellitimide benzoyl thiourea cross-linked chitosan (PIBTU-CS) hydrogel, was evaluated as a green biocatalyst for the efficient synthesis of novel thiazole derivatives. The PIBTU-CS hydrogel showcased key advantages, such as an expanded surface area and superior thermal stability, establishing it as a potent eco-friendly catalyst. By employing PIBTU-CS alongside ultrasonic irradiation, we successfully synthesized a series of novel thiazoles through the reaction of 2-(4-((2-carbamothioylhydrazineylidene)methyl)phenoxy)-N-(4-chlorophenyl)acetamide with a variety of hydrazonoyl halides (6af) and α-haloketones (8ac or 10a,b). A comparative analysis with TEA revealed that PIBTU-CS hydrogel consistently delivered significantly higher yields. This synthetic strategy provided several benefits, including mild reaction conditions, reduced reaction times, and consistently high yields. The robustness of PIBTU-CS was further underscored by its ability to be reused multiple times without a substantial reduction in catalytic efficiency. The structures of the synthesized thiazole derivatives were meticulously characterized using a range of analytical techniques, including IR, 1H-NMR, 13C-NMR, and mass spectrometry (MS), confirming their successful formation. These results underscore the potential of PIBTU-CS hydrogel as a sustainable and recyclable catalyst for the synthesis of heterocyclic compounds. Additionally, all synthesized products were tested for their anticancer activity against HepG2-1 cells, with several new compounds exhibiting good anticancer effects. Full article
(This article belongs to the Special Issue Catalytic Energy Conversion and Catalytic Environmental Purification)
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Graphical abstract

Graphical abstract
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<p>Examples of thiazole-bearing anticancer drugs.</p>
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<p>TG analysis of chitosan and PIBTU-CS hydrogel.</p>
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<p>Cytotoxic effects of the tested compounds on HEPG2-1 cells.</p>
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<p>Synthesis of PIBTU-CS hydrogel.</p>
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<p>Synthesis of arylazothiazoles <b>7a</b>–<b>f</b>.</p>
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<p>Proposed mechanism for synthesis of arylazothiazoles <b>7a</b>–<b>f</b>.</p>
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<p>Synthesis of thiazoles <b>9a</b>–<b>c</b> and <b>11a</b>,<b>b</b>.</p>
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22 pages, 2134 KiB  
Article
Unlocking Economic and Environmental Gains Through Lithium-Ion Battery Recycling for Electric Vehicles
by Bianca Ifeoma Chigbu and Ikechukwu Umejesi
Resources 2024, 13(12), 163; https://doi.org/10.3390/resources13120163 - 21 Nov 2024
Viewed by 248
Abstract
Amid South Africa’s shift towards electric vehicles (EVs), building a lithium-ion battery (LIB) recycling sector is essential for promoting sustainable development and generating employment opportunities. This study employs qualitative methodologies to collect insights from 12 critical stakeholders in the automotive, mining, and recycling [...] Read more.
Amid South Africa’s shift towards electric vehicles (EVs), building a lithium-ion battery (LIB) recycling sector is essential for promoting sustainable development and generating employment opportunities. This study employs qualitative methodologies to collect insights from 12 critical stakeholders in the automotive, mining, and recycling sectors and academia to examine the feasibility and advantages of establishing such an industry. We implemented purposeful and snowball sampling to guarantee an exhaustive array of viewpoints. Thematic analysis of the interview data reveals that LIB recycling has substantial social, environmental, and economic implications. The results emphasize the pressing necessity of recycling infrastructure to mitigate environmental impacts and attract investment. The economic feasibility and employment potential of LIB recycling is promising despite the early stage of the EV industry in South Africa. These potentials are influenced by EV adoption rates, technological advancements, regulatory frameworks, and industry growth. In this sector, employment opportunities are available in various phases: battery collection, transportation, disassembly, testing, mechanical crushing, hydrometallurgical processes, valuable metal recovery, manufacturing, reuse, research and development, and administrative roles. Each of these roles necessitates a unique set of skills. This interdisciplinary research investigates vital elements of economic growth, employment creation, environmental sustainability, policymaking, technological innovation, and global collaboration. The study offers valuable guidance to policymakers and industry stakeholders trying to establish a sustainable and robust LIB recycling industry in South Africa by utilizing Transition Management Theory to develop a framework for improving the sustainability and circularity of the EV LIB recycling sector. Full article
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<p>Flowchart of the EV LIB Recycling Process.</p>
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<p>Theoretical Foundations for LIB Recycling: A Sustainable Approach.</p>
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<p>LIB recycling landscape.</p>
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<p>Employment creation in LIB recycling sector.</p>
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<p>Practical insights and beneficiaries.</p>
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24 pages, 3313 KiB  
Article
Evaluation of Biogas Production from Anaerobic Digestion of Biopolymeric Films and Potential Environmental Implications
by Nicolò Montegiove, Roberto Petrucci, Leonardo Bacci, Giovanni Gigliotti, Debora Puglia, Luigi Torre and Daniela Pezzolla
Sustainability 2024, 16(22), 10146; https://doi.org/10.3390/su162210146 (registering DOI) - 20 Nov 2024
Viewed by 331
Abstract
The increasing environmental pollution resulting from plastic waste and the need to reuse agro-industrial wastes as a source of discarding has led to the development of innovative biobased products. In the frame of this context, the use of neat polylactic acid (PLA) and [...] Read more.
The increasing environmental pollution resulting from plastic waste and the need to reuse agro-industrial wastes as a source of discarding has led to the development of innovative biobased products. In the frame of this context, the use of neat polylactic acid (PLA) and its blend with polybutylene succinate (PBS) with or without cellulose nanocrystals (CNCs) extracted from hemp fibers is explored here. This study aimed to assess the biogas production of different biopolymeric films. In parallel, life cycle assessment (LCA) analysis was performed on the same films, focusing on their production phase and potential end-of-life scenarios, regardless of film durability (i.e., single-use packaging) and barrier performance, to counteract possible soil health threats. Specifically, this study considered three specific systems: PLA, PLA_PBS (PLA/PBS blend 80:20 w/w), and PLA_PBS_3CNC (PLA/PBS blend + 3% CNCs) films. The assessment involved a batch anaerobic digestion (AD) process at 52 °C, using digestate obtained from the anaerobic treatment of municipal waste as the inoculum and cellulose as a reference material. The AD process was monitored over about 30 days, revealing that reactors containing cellulose showed inherent biodegradability and enhanced biogas production. On the other hand, biopolymeric films based on PLA and its blends with PBS and CNCs exhibited an inhibitory effect, likely due to their recalcitrant nature, which can limit or delay microbial activity toward biomass degradation and methanogenesis. LCA analysis was performed taking into consideration the complex environmental implications of both including biopolymers in the production of renewable energy and the use of post-composting digestate as an organic fertilizer. Remarkably, the PLA_PBS_3CNC formulation revealed slightly superior performance in terms of biodegradability and biogas production, mainly correlated to the presence of CNCs in the blend. The observed enhanced biodegradability and biogas yield, coupled with the reduced environmental impact, confirm the key role of optimized biopolymeric formulations in mitigating inhibitory effects on AD processes while maximizing, at the same time, the utilization of naturally derived energy sources. Full article
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<p>Schematic representation of the film production through extrusion and casting.</p>
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<p>Representation of a laboratory-scale anaerobic digestion reactor connected to a hydraulic gasometer. The quantification of the volume of biogas produced is obtained by measuring the volume of displaced water.</p>
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<p>Cumulative biogas production after 27-day thermophilic anaerobic digestion of the sole inoculum, inoculum and cellulose films, inoculum and PLA films, inoculum and PLA/PBS-blended films, and inoculum and PLA/PBS-blended films added with CNCs, expressed as Nm<sup>3</sup> of biogas per ton of total solids (SEM = 5.663).</p>
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<p>Biodegradation kinetics of biopolymeric films fitted to the modified Gompertz model following 27-day thermophilic anaerobic digestion expressed as biodegradation % into CO<sub>2</sub> and CH<sub>4</sub>.</p>
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<p>Comparison of the LCA score obtained for the investigated system, analyzed by means of the ReCiPe 2016 Endpoint (H) tool.</p>
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<p>Process tree and LCA score related to the film based on PLA biopolymer. Cut-off 0.50%.</p>
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<p>Process tree and LCA score related to the film based on PLA/PBS blend. Cut-off 0.50%.</p>
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<p>Process tree and LCA score related to the film based on PLA/PBS blend reinforced with CNCs. Cut-off 0.50%.</p>
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<p>Most important impact categories in the case of the investigated systems.</p>
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<p>Most important environmental burdens in the case of the investigated systems.</p>
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18 pages, 3743 KiB  
Article
Efficient Reuse of Rare Earth Carbonate Precipitation Mother Liquor for Rare Earth Leaching in Strong Acid-Restricted Area
by Jian Feng, Xiaoyan Wu, Fang Zhou and Ruan Chi
Minerals 2024, 14(11), 1179; https://doi.org/10.3390/min14111179 - 20 Nov 2024
Viewed by 227
Abstract
Due to the restrictions of strong acids in some regions, the reuse process of rare earth (RE) precipitation mother liquor is difficult to carry out. To achieve the straightforward and efficient reuse of precipitation mother liquor in such areas, the potential for directly [...] Read more.
Due to the restrictions of strong acids in some regions, the reuse process of rare earth (RE) precipitation mother liquor is difficult to carry out. To achieve the straightforward and efficient reuse of precipitation mother liquor in such areas, the potential for directly reusing this liquor for rare earth (RE) leaching was explored. The results showed that when the RE concentration in the leachate ranged from 0.1 to 1.5 g/dm3 and the RE precipitation rate exceeded 96%, the residual total carbonate content in precipitation mother liquor was less than 0.01 mol/L, and the solution pH was 7–8. Furthermore, when the total carbonate content in leaching liquor was lower than 0.01 mol/L, the presence of carbonate had a minimal impact on the RE leaching efficiency, which was observed to exceed 93%. Additionally, the process of mother liquor leaching was analyzed using dynamic models and chromatography tray theory. It was found that the leaching results were well fitted with the shrinking core model, and the apparent activation energy of RE was 5.77 kJ/mol, indicating that the reaction was controlled by diffusion, and the reaction order was 0.672 for RE. This confirms that a total carbonate content below 0.01 mol/L in the precipitation mother liquor can be directly used for the RE leaching process. Full article
(This article belongs to the Special Issue Green and Efficient Recovery/Extraction of Rare Earth Resources)
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<p>Schematic diagram of experimental apparatus.</p>
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<p>XRD diffraction pattern of the RE ore.</p>
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<p>Effect of the dosage of ammonium bicarbonate on RE precipitation rate (■), residual total carbonate content (▲), and pH (●) (RE concentration: (<b>a</b>) 0.118 g/dm<sup>3</sup>, (<b>b</b>) 0.227 g/dm<sup>3</sup>, (<b>c</b>) 0.441 g/dm<sup>3</sup>, (<b>d</b>) 0.676 g/dm<sup>3</sup>, (<b>e</b>) 0.965 g/dm<sup>3</sup>, (<b>f</b>) 1.470 g/dm<sup>3</sup>).</p>
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<p>Effect of the dosage of ammonium bicarbonate on RE precipitation rate (■), residual total carbonate content (▲), and pH (●) (RE concentration: (<b>a</b>) 0.118 g/dm<sup>3</sup>, (<b>b</b>) 0.227 g/dm<sup>3</sup>, (<b>c</b>) 0.441 g/dm<sup>3</sup>, (<b>d</b>) 0.676 g/dm<sup>3</sup>, (<b>e</b>) 0.965 g/dm<sup>3</sup>, (<b>f</b>) 1.470 g/dm<sup>3</sup>).</p>
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<p>Effect of RE concentration on ammonium bicarbonate dosage when RE precipitation rate reached equilibrium and RE precipitation rate in the process of recovering rare earth from leachate (molar ratio of ammonium bicarbonate was 4:1).</p>
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<p>Effect of total carbonate content on RE leaching efficiency and pH of the leachate.</p>
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<p>RE leaching efficiency and pH of leachate of different leaching solutions: #1 was 2% ammonium sulfate, #2–#7, respectively, represented the precipitation mother liquor in <a href="#minerals-14-01179-f003" class="html-fig">Figure 3</a>a–f.</p>
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<p>Φ-pH diagram of ammonium bicarbonate in the aqueous solution.</p>
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<p>pM-pH diagram of ammonium bicarbonate precipitation system.</p>
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<p>Effect of the total bicarbonate concentration on the kinetic curves of RE.</p>
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<p>The relationship between ln<span class="html-italic">k</span> and ln<span class="html-italic">C</span><sub>0</sub>.</p>
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<p>Effect of temperature on the kinetic curves of RE.</p>
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<p>The relationship between plots of ln<span class="html-italic">k</span> versus 1/T.</p>
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<p>Effect of the total bicarbonate concentration on the leaching curves of RE.</p>
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<p>Effect of the leaching temperature on the leaching curves of RE.</p>
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16 pages, 7984 KiB  
Article
Efficient Catalytic Reduction of Organic Pollutants Using Nanostructured CuO/TiO2 Catalysts: Synthesis, Characterization, and Reusability
by Mariyem Abouri, Abdellah Benzaouak, Fatima Zaaboul, Aicha Sifou, Mohammed Dahhou, Mohammed Alaoui El Belghiti, Khalil Azzaoui, Belkheir Hammouti, Larbi Rhazi, Rachid Sabbahi, Mohammed M. Alanazi and Adnane El Hamidi
Inorganics 2024, 12(11), 297; https://doi.org/10.3390/inorganics12110297 - 19 Nov 2024
Viewed by 454
Abstract
The catalytic reduction of organic pollutants in water is a critical environmental challenge due to the persistent and hazardous nature of compounds like azo dyes and nitrophenols. In this study, we synthesized nanostructured CuO/TiO2 catalysts via a combustion technique, followed by calcination [...] Read more.
The catalytic reduction of organic pollutants in water is a critical environmental challenge due to the persistent and hazardous nature of compounds like azo dyes and nitrophenols. In this study, we synthesized nanostructured CuO/TiO2 catalysts via a combustion technique, followed by calcination at 700 °C to achieve a rutile-phase TiO2 structure with varying copper loadings (5–40 wt.%). The catalysts were characterized using X-ray diffraction (XRD), attenuated total reflectance-Fourier transform infrared (ATR–FTIR) spectroscopy, thermogravimetric analysis-differential thermal analysis (TGA–DTA), UV-visible diffuse reflectance spectroscopy (DRS), and scanning electron microscopy with energy-dispersive X-ray spectroscopy (SEM–EDS). The XRD results confirmed the presence of the crystalline rutile phase in the CuO/TiO2 catalysts, with additional peaks indicating successful copper oxide loading onto TiO2. The FTIR spectra confirmed the presence of all the functional groups in the prepared samples. SEM images revealed irregularly shaped copper oxide and agglomerated TiO2 particles. The DRS results revealed improved optical properties and a decreased bandgap with increased Cu content, and 4-Nitrophenol (4-NP) and methyl orange (MO), which were chosen for their carcinogenic, mutagenic, and nonbiodegradable properties, were used as model organic pollutants. Catalytic activities were tested by reducing 4-NP and MO with sodium borohydride (NaBH4) in the presence of a CuO/TiO2 catalyst. Following the in situ reduction of CuO/TiO2, Cu (NPs)/TiO2 was formed, achieving 98% reduction of 4-NP in 480 s and 98% reduction of MO in 420 s. The effects of the NaBH4 concentration and catalyst mass were investigated. The catalysts exhibited high stability over 10 reuse cycles, maintaining over 96% efficiency for MO and 94% efficiency for 4-NP. These findings demonstrate the potential of nanostructured CuO/TiO2 catalysts for environmental remediation through efficient catalytic reduction of organic pollutants. Full article
(This article belongs to the Special Issue New Advances into Nanostructured Oxides, 2nd Edition)
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<p>XRD patterns of different wt.% CuO/TiO<sub>2</sub> samples.</p>
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<p>XRD patterns of 40 wt.% CuO/TiO<sub>2</sub> samples calcined at different temperatures.</p>
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<p>XRD patterns of 40 wt.% CuO/TiO<sub>2</sub> before and after the reduction experiment.</p>
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<p>Thermal curves of the as-prepared 40 wt.% CuO/TiO<sub>2</sub> without calcination under air flow at 10 °C min<sup>−1</sup>.</p>
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<p>Infrared spectra of the wt.% CuO/TiO<sub>2</sub> samples.</p>
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<p>(<b>a</b>) UV–vis diffuse reflectance spectra of TiO<sub>2</sub> and wt.% CuO/TiO<sub>2</sub> and (<b>b</b>) Tauc plot.</p>
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<p>SEM micrographs of 40 wt.% CuO/TiO<sub>2</sub>.</p>
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<p>EDS Spectrum of 40 wt.% CuO/TiO<sub>2</sub>.</p>
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<p>EDX mapping of the 40 wt.% CuO/TiO<sub>2</sub> catalyst.</p>
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<p>Reduction performance of the wt.% CuO/TiO<sub>2</sub> catalysts for 4-NP (<b>a</b>) and MO (<b>b</b>).</p>
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<p>UV–vis spectra of the reduction of (<b>a</b>) 4-NP and (<b>b</b>) MO by NaBH<sub>4</sub> without the catalyst and absorbance spectra of (<b>c</b>) 4-NP and (<b>d</b>) MO in the presence of NaBH<sub>4</sub> and CuO/TiO<sub>2</sub>.</p>
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<p>UV–vis spectra of the reduction of (<b>a</b>) 4-NP and (<b>b</b>) MO by NaBH<sub>4</sub> without the catalyst and absorbance spectra of (<b>c</b>) 4-NP and (<b>d</b>) MO in the presence of NaBH<sub>4</sub> and CuO/TiO<sub>2</sub>.</p>
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<p>First-order plot for the catalytic reduction of (<b>a</b>) 4-NP and (<b>b</b>) MO. Experimental conditions: 40 wt.% CuO/TiO<sub>2</sub> dose = 0.04 g/L, [NaBH<sub>4</sub>] = 14 mM, and [4-NP or MO] = 0.35 mM.</p>
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<p>Schematic reactions of (<b>a</b>) 4-NP and (<b>b</b>) MO, by NaBH<sub>4</sub> in the presence of Cu(NPs)/TiO<sub>2</sub>.</p>
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<p>Pollutant removal versus time plots for catalytic reduction using 40 wt.% CuO/TiO<sub>2</sub>, showing the effect of catalyst dose on the reduction of (<b>a</b>) 4-NP and (<b>b</b>) MO, and the effect of NaBH<sub>4</sub> concentration on the reduction of (<b>c</b>) 4-NP and (<b>d</b>) MO.</p>
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<p>Recycling of CuO/TiO<sub>2</sub> in the hydrogenation of (<b>a</b>) 4-NP and (<b>b</b>) MO.</p>
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<p>Synthesis procedure for the catalysts.</p>
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<p>Catalytic reduction experiments of organic pollutants.</p>
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14 pages, 16495 KiB  
Article
Research on the Reusability of Bentonite Waste Materials for Residual Chlorine Removal
by Ieva Andriulaityte, Marina Valentukeviciene and Ramune Zurauskiene
Materials 2024, 17(22), 5647; https://doi.org/10.3390/ma17225647 - 19 Nov 2024
Viewed by 323
Abstract
Recyclable construction waste can be used as a low-cost material to reduce stormwater pollution caused by various pollutants. In recent years, studies have reported increased water contamination from chlorine and chlorine compounds and its negative impact on aquatic ecosystems. When assessing the need [...] Read more.
Recyclable construction waste can be used as a low-cost material to reduce stormwater pollution caused by various pollutants. In recent years, studies have reported increased water contamination from chlorine and chlorine compounds and its negative impact on aquatic ecosystems. When assessing the need for waste recycling, circularity, and stormwater reuse, it is worth evaluating the capacities of construction waste materials to reduce stormwater pollution from residual chlorine. Laboratory experiments using bentonite waste material (bentonite clay) and sodium hypochlorite solutions were carried out to analyze the potential of bentonite clay to retain residual chlorine in stormwater and evaluate its capacity to be applied as filtration media in green infrastructure. In the first stage, the particle size distribution and texture of bentonite clay were assessed using laboratory sieve analysis and microscopy. The results of the experiments indicated that the optimal grain size to retain pollutants was 0.8–2.0 mm. The microstructure analysis showed the capacity of bentonite to retain residual chlorine. The results of the static and dynamic experiments (leaching and filtration tests) show that the bentonite clay retained up to 44% of the residual chlorine. The obtained results indicate that bentonite clay might be suitable for application as filtration media in green infrastructure to reduce stormwater contamination. Full article
(This article belongs to the Special Issue Recycling and Sustainability of Industrial Solid Waste)
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<p>Order of experiments.</p>
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<p>Sieve analysis test: (<b>a</b>) seven calibrated sieves with mesh sizes of 500 µm, 600 µm, 800 µm, 1000 µm, 1600 µm, 2000 µm, and 2500 µm; (<b>b</b>) testing material after separation through the sieves.</p>
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<p>Scheme of filtration test set-up.</p>
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<p>The distribution curve of the bentonite clay’s grain sizes.</p>
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<p>Test samples of bentonite clay suitable for filtration: (<b>a</b>) 0.8 mm; (<b>b</b>) 1.0 mm; (<b>c</b>) 1.6 mm; (<b>d</b>) 2.0 mm.</p>
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<p>Microstructure analysis of the surface structure of bentonite clay before interacting with the sodium hypochlorite solution (enlarged 80 times).</p>
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<p>Microstructure analysis of bentonite clay surface structure after interacting with sodium hypochlorite solution (enlarged 80 times).</p>
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<p>Microstructure analysis of bentonite clay surface structure after interacting with sodium hypochlorite solution (enlarged 80 times).</p>
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<p>Changes in stormwater indicators depending on disinfectant concentrations.</p>
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13 pages, 7177 KiB  
Article
Preparation of an FA-Based Discoloration Material and Its Application in Jewelry Design
by Xiaomin Zhang, Xiangrui Gao, Yue Yuan, Guangqin Yang and Yanchen Li
Materials 2024, 17(22), 5628; https://doi.org/10.3390/ma17225628 - 18 Nov 2024
Viewed by 464
Abstract
Fly ash (FA) is the main solid waste emitted from coal-fired power plants. Due to its high yield, low utilization rate, and occupation of a large amount of land, it exerts enormous pressure on the Earth’s environment. With the deepening of the concept [...] Read more.
Fly ash (FA) is the main solid waste emitted from coal-fired power plants. Due to its high yield, low utilization rate, and occupation of a large amount of land, it exerts enormous pressure on the Earth’s environment. With the deepening of the concept of sustainable development, exploring the reuse of industrial waste such as FA has become a key strategy. If FA can be combined with commonly used jewelry in people’s lives, it will be of great significance to promote the high-net-worth utilization of FA. Therefore, this study synthesized a fly-ash-based composite material with color-changing function and combined it with necklaces as the main material. In the first stage, after blending fly ash and slag, an alkaline activator with a total mass of 10% was added. When the proportion of fly ash was 60%, the compressive strength of the prepared fly-ash-based composite material reached 10.1 MPa. This was attributed to the reaction between sodium silicate in the alkaline activator and free CaO, MgO, and other substances in the fly ash to form hydrated silicate colloids, which solidify the fly ash and transform it into a complex three-dimensional network skeleton. In the second stage, a UV resistant coating with thermochromic function was obtained by blending acrylic resin, TiO2, and a thermosensitive color-changing agent. It was applied to the surface of fly-ash-based composite materials, and the results showed that as the content of the color-changing agent increased, the number of pores on the surface of the coating gradually decreased. When the content of color-changing agent was 10%, the prepared 10%FAB not only had good surface color but also had good thermal stability, UV absorption ability, superhydrophobicity, and mechanical properties. Therefore, 10%FAB was selected as the basic material for jewelry design. In the third stage, the traditional Chinese technique of “gold inlaid with jade” was utilized to develop jewelry applications for the FA composites. As such, 10%FAB was processed into necklaces, which not only had modern design aesthetics but also had good color-changing effects above 30 °C. And after a long period of UV aging experiments, the necklace did not show any wrinkles, bubbles, or other phenomena. Due to the excitation of TiO2 hole–electron pairs, the necklace’s UV absorption ability was further improved. This study demonstrates the potential application of industrial waste in decorative products, expands the high-end utilization of fly ash as a low-cost material, and provides new ideas for building a low-carbon lifestyle. Full article
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<p>Appearance and disordered storage of FA.</p>
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<p>Preparation of FA-based composites and surface treatment.</p>
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<p>Preparation process of color-changing FA-based necklace of (<b>a</b>) Desgn drawing; (<b>b</b>) computer edition; (<b>c</b>) spraying; (<b>d</b>) wax reverse mold; (<b>e</b>) die repair model; (<b>f</b>) inlaid stone; (<b>g</b>) combined welding; (<b>h</b>) polishing; (<b>i</b>) electroplating; (<b>j</b>) inlaid stone; (<b>k</b>) finished product.</p>
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<p>(<b>a</b>) Compressive properties of FA-based composites; (<b>b</b>) micro-morphology of FA-based composites; (<b>c</b>) gelation effect of FA-based composites.</p>
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<p>Microscopic morphology of (<b>a</b>) 0%Film; (<b>b</b>) 5%Film; (<b>c</b>) 10%Film and (<b>d</b>) 20%Film. (<b>e</b>) thermogravimetric analysis of the films; (<b>f</b>) comparison of thermal degradation rates of the films.</p>
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<p>(<b>a</b>) XRD pattern of surface coating; (<b>b</b>) compressive strength test of FAB after coating treatment.</p>
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<p>(<b>a</b>) UV-Vis absorption spectrum of FAB; (<b>b</b>) Microstructure of FA composite.</p>
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<p>(<b>a</b>) Water absorption curve of FAB; (<b>b</b>) water contact angle of 5%FAB; (<b>c</b>) water contact angle of 10%FAB; (<b>d</b>) water contact angle of 20%FAB.</p>
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<p>Color change effect of (<b>a</b>) 0%FAB; (<b>b</b>) 5%FAB; (<b>c</b>) 10%FAB; (<b>d</b>) 20%FAB.</p>
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<p>Color change effect of FA-based necklace.</p>
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<p>(<b>a</b>) Surface of necklaces before UV aging; (<b>b</b>) surface of necklaces after UV aging; (<b>c</b>) comparison of UV light absorption capacity of necklaces before and after aging.</p>
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36 pages, 13266 KiB  
Review
Airborne Microplastics: Challenges, Prospects, and Experimental Approaches
by Alexey R. Rednikin, Yulia A. Frank, Artem O. Rozhin, Danil S. Vorobiev and Rawil F. Fakhrullin
Atmosphere 2024, 15(11), 1380; https://doi.org/10.3390/atmos15111380 - 15 Nov 2024
Viewed by 1102
Abstract
Airborne microplastics are emerging pollutants originating from disposable tableware, packaging materials, textiles, and other consumer goods. Microplastics vary in shape and size and exposed to external factors break down into even smaller fractions. Airborne microplastics are abundant in both urban and natural environments, [...] Read more.
Airborne microplastics are emerging pollutants originating from disposable tableware, packaging materials, textiles, and other consumer goods. Microplastics vary in shape and size and exposed to external factors break down into even smaller fractions. Airborne microplastics are abundant in both urban and natural environments, including water bodies and glaciers, as particles can travel long distances. The potential toxicity of airborne microplastics cannot be underestimated. Microparticles, especially those < 10 µm, entering the human body through inhalation or ingestion have been shown to cause serious adverse health effects, such as chronic inflammation, oxidation stress, physical damage to tissues, etc. Microplastics adsorb toxic chemicals and biopolymers, forming a polymer corona on their surface, affecting their overall toxicity. In addition, microplastics can also affect carbon dynamics in ecosystems and have a serious impact on biochemical cycles. The approaches to improve sampling techniques and develop standardized methods to assess airborne microplastics are still far from being perfect. The mechanisms of microplastic intracellular and tissue transport are still not clear, and the impact of airborne microplastics on human health is not understood well. Reduced consumption followed by collection, reuse, and recycling of microplastics can contribute to solving the microplastic problem. Combinations of different filtration techniques and membrane bioreactors can be used to optimize the removal of microplastic contaminants from wastewater. In this review we critically summarize the existing body of literature on airborne microplastics, including their distribution, identification, and safety assessment. Full article
(This article belongs to the Section Air Quality)
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<p>Bright field microscopy images of different types of MPs: (<b>a</b>) fiber, (<b>b</b>) foam, (<b>c</b>,<b>d</b>) film, (<b>e</b>) fragment, (<b>f</b>) microsphere. (<b>a1</b>,<b>b1</b>,<b>c1</b>,<b>d1</b>,<b>e1</b>,<b>f1</b>) are the corresponding fluorescence micrographs [<a href="#B80-atmosphere-15-01380" class="html-bibr">80</a>].</p>
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<p>Chemical structure of common MP components: polypropylene (<b>1</b>) and polystyrene (<b>2</b>).</p>
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<p>Mean daily AMP deposition (m<sup>−2</sup> d<sup>−1</sup>) by region (based on the published data, <a href="#app1-atmosphere-15-01380" class="html-app">Table S1</a>)—(<b>a</b>); proportion of DAMPs in urban areas and in remote areas, %—(<b>b</b>).</p>
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<p>Interaction between AMPs and the human body.</p>
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<p>Stages in studying AMPs: Step 1—Sampling by active (<b>a</b>) or passive (<b>b</b>) methods; Step 2—Laboratory processing with density separation (<b>c</b>) and digestion (<b>d</b>); Step 3—Particle analysis: quantitative counting, determination of size, shape, color (<b>e</b>) and polymer identification (<b>f</b>).</p>
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30 pages, 9808 KiB  
Article
Multi-Criteria Analysis for Geospatialization of Potential Areas for Water Reuse in Irrigated Agriculture in Hydrographic Regions
by Ana Paula Pereira Carvalho, Ana Claudia Pereira Carvalho, Mirian Yasmine Krauspenhar Niz, Fabrício Rossi, Giovana Tommaso and Tamara Maria Gomes
Agronomy 2024, 14(11), 2689; https://doi.org/10.3390/agronomy14112689 - 15 Nov 2024
Viewed by 439
Abstract
As the climate crisis progresses, droughts and the seasonal availability of fresh water are becoming increasingly common in different regions of the world. One solution to tackle this problem is the reuse of treated wastewater in agriculture. This study was carried out in [...] Read more.
As the climate crisis progresses, droughts and the seasonal availability of fresh water are becoming increasingly common in different regions of the world. One solution to tackle this problem is the reuse of treated wastewater in agriculture. This study was carried out in two significant hydrographic regions located in the southeast of Brazil (Mogi Guaçu River Water Management Unit—UGRHI-09 and Piracicaba River Basin—PRB) that have notable differences in terms of land use and land cover. The aim of this study was to carry out a multi-criteria analysis of a set of environmental attributes in order to classify the areas under study according to their levels of soil suitability and runoff potential. The integrated analysis made it possible to geospatialize prospective regions for reuse, under two specified conditions. In the UGRHI-09, condition 1 corresponds to 3373.24 km2, while condition 2 comprises 286.07 km2, located mainly in the north-western and central-eastern portions of the unit. In the PRB, condition 1 was also more expressive in occupational terms, corresponding to 1447.83 km2; and condition 2 was perceptible in 53.11 km2, predominantly in the central region of the basin. The physical characteristics of the areas studied were decisive in delimiting the areas suitable for the reuse of treated wastewater. Full article
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<p>Location of study areas. Land use and land cover maps of UGRHI-09 (<b>A</b>) and PRB (<b>B</b>). Source: Adapted from [<a href="#B45-agronomy-14-02689" class="html-bibr">45</a>,<a href="#B46-agronomy-14-02689" class="html-bibr">46</a>].</p>
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<p>Methodological steps developed in the study. * So: soils (type, texture and thickness). It is worth noting that the PRB runoff levels were mapped by [<a href="#B47-agronomy-14-02689" class="html-bibr">47</a>].</p>
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<p>Slope chart of UGRHI-09 (<b>a</b>) and PRB (<b>b</b>).</p>
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<p>Elevation map of UGRHI-09 (<b>a</b>) and PRB (<b>b</b>).</p>
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<p>Soil maps of UGRHI-09 (<b>a</b>) and PRB (<b>b</b>).</p>
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<p>Drainage density map of UGRHI-09 (<b>a</b>) and PRB (<b>b</b>) [<a href="#B47-agronomy-14-02689" class="html-bibr">47</a>].</p>
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<p>Geology map of UGRHI-09 (<b>a</b>) and PRB (<b>b</b>).</p>
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<p>Depth of groundwater level map of UGRHI-09 (<b>a</b>) and PRB (<b>b</b>).</p>
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<p>Drainage network map of UGRHI-09 (<b>a</b>) and PRB (<b>b</b>); distance to stream map of UGRHI-09 (<b>c</b>) and PRB (<b>d</b>).</p>
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<p>Random Consistency Index values considering the order of the matrix.</p>
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<p>Normalized matrices considering the environmental attributes of the LSC and the SRPC.</p>
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<p>Final weights of environmental attributes used to prepare interpretative cartographic products.</p>
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<p>Descriptions of potential areas for the reuse of treated wastewater from agro-industrial sources in irrigation.</p>
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<p>Map of inapt areas at UGRHI-09 (<b>a</b>) and PRB (<b>b</b>).</p>
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<p>UGRHI-09 Land Suitability Chart (<b>a</b>), PRB Land Suitability Chart (<b>b</b>), UGRHI-09 Surface Runoff Potential Chart (<b>c</b>), and PRB Surface Runoff Potential Chart (<b>d</b>).</p>
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<p>Decadal average rainfall (2013 to 2022) (<b>a</b>), decadal average actual evapotranspiration (2013 to 2022) (<b>b</b>), and the difference between the decadal average rainfall and the decadal average actual evapotranspiration (<b>c</b>).</p>
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<p>Potential areas in UGRHI-09 (<b>a</b>) and PRB (<b>b</b>) for adopting the practice of reusing treated wastewater from agro-industries.</p>
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19 pages, 3575 KiB  
Article
Contributions to Incorporation of Non-Recyclable Plastics in Bituminous Mixtures
by João Fonseca, Vítor Antunes and Ana Cristina Freire
Sustainability 2024, 16(22), 9945; https://doi.org/10.3390/su16229945 - 14 Nov 2024
Viewed by 440
Abstract
Over the past 50 years, global plastic production has surged exponentially. Around 40% of this plastic is used for packaging, most of which is single-use, while 20% is used in construction. Despite the vast quantities produced, only about 6% of discarded plastics are [...] Read more.
Over the past 50 years, global plastic production has surged exponentially. Around 40% of this plastic is used for packaging, most of which is single-use, while 20% is used in construction. Despite the vast quantities produced, only about 6% of discarded plastics are properly recycled, 10% are incinerated, and the majority are disposed of without proper management. With low recycling rates and some plastics being non-recyclable or with limited recycling cycles, it is important to explore new ways of reusing this waste as secondary raw materials. This study explores the potential of incorporating non-recyclable plastic waste into bituminous mixtures. The objective is to develop a sustainable solution for surface courses with similar or better performance than traditional bituminous mixtures by incorporating plastic waste using the dry method. A bituminous mixture containing 10% non-recyclable plastic was formulated and tested for water sensitivity, wheel tracking, and stiffness modulus. Additionally, environmental and economic comparisons were performed with a standard surface mixture. Results showed increased water resistance, high resistance to permanent deformation, reduced stiffness, lower susceptibility to frequency and temperature variations, and greater flexibility. These findings suggest that adding plastic not only enhances mechanical properties but also reduces costs, offering a sustainable alternative for non-recyclable plastics in road construction. Full article
(This article belongs to the Section Sustainable Engineering and Science)
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<p>Plastic sample.</p>
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<p>Representative constituents: presentation and percentages.</p>
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<p>Grading curve.</p>
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<p>Melting point at 120 °C.</p>
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<p>(<b>a</b>) Porosity; (<b>b</b>) Marshall stability; (<b>c</b>) VMA; (<b>d</b>) deformation.</p>
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<p>(<b>a</b>) Porosity; (<b>b</b>) Marshall stability; (<b>c</b>) VMA; (<b>d</b>) deformation.</p>
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<p>Evaluation of water sensitivity: (<b>a</b>) indirect tensile strength in dry and wet conditions; (<b>b</b>) indirect tensile strength ratio.</p>
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<p>Permanent deformation.</p>
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<p>(<b>a</b>) Stiffness modulus; (<b>b</b>) phase angle; (<b>c</b>) storage modulus (E<sub>1</sub>); (<b>d</b>) loss modulus (E<sub>2</sub>).</p>
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<p>Cost analysis of bituminous mixtures components.</p>
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18 pages, 3451 KiB  
Article
Comparative Analysis of Sewage Sludge Characteristics After Natural Deposition, Accelerated Aging, and Composting
by Elena Gogina, Nikolay Makisha and Igor Gulshin
Appl. Sci. 2024, 14(22), 10446; https://doi.org/10.3390/app142210446 - 13 Nov 2024
Viewed by 408
Abstract
This study investigated treatment methods for urban wastewater sludge, specifically examining natural drying over five years, accelerated freeze–thaw–drying cycles, and composting with and without a zeolite additive. The findings reveal that composting effectively stabilized the sludge while retaining essential nutrients crucial for agriculture. [...] Read more.
This study investigated treatment methods for urban wastewater sludge, specifically examining natural drying over five years, accelerated freeze–thaw–drying cycles, and composting with and without a zeolite additive. The findings reveal that composting effectively stabilized the sludge while retaining essential nutrients crucial for agriculture. Notably, with the addition of 2% zeolite by total mass, approximately 40% of the total nitrogen was preserved. Adequate aeration during composting maintained acceptable levels of phosphorus compounds, with the phosphorus content expressed as P2O5 showing significant retention compared with the natural drying methods. Composting also demonstrated a substantial reduction in petroleum hydrocarbon concentrations, which decreased from 30 mg/kg to 3 mg/kg, thereby showcasing its potential for processing contaminated sludge. The inclusion of zeolite enhanced the nitrogen retention by an additional 10–20% compared with the composting without zeolite, aligning with previous studies on its effectiveness. While composting and thermal treatments, like accelerated freeze–thaw cycles, influenced the physical properties of the sludge—such as reducing the moisture content and altering the volatile substance concentrations—they did not significantly affect the heavy metal levels. Natural drying over five years resulted in reduced metal quantities, which possibly reflected changes in the wastewater characteristics over time. Given that the heavy metal concentrations remained largely unchanged, additional treatment methods are recommended when the initial sludge contains high levels of these contaminants to ensure the safe use of the final product as fertilizer. This study underscored the significant role of biochemical and microbiological processes during composting and natural drying in transforming sludge properties. Future research should focus on establishing upper contamination thresholds and exploring microbiological safety measures to enhance the viability of sludge reuse in agriculture, balancing nutrient preservation with environmental safety. Full article
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<p>Zeolite used for sludge mixture before composting.</p>
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<p>The examined sludge: (<b>a</b>) collection after dewatering; (<b>b</b>) collection from the disposal site; (<b>c</b>) sludge that underwent freeze–thaw–drying cycles.</p>
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<p>Laboratory reactor used in the wastewater treatment efficiency evaluation phase: (<b>a</b>) reaction vessel containing the composting mixture; (<b>b</b>) water baths in heating mode with the reaction vessels.</p>
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<p>Temperature profile of composting: (1) heating phase; (2) thermophilic stage; (3) mesophilic stage; (4) cooling of the compost.</p>
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<p>Boxplots for ash content in the samples.</p>
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<p>Boxplots for pH in the samples.</p>
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<p>Boxplots for ammonium in the samples.</p>
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<p>Boxplots for phosphates in the samples.</p>
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<p>Boxplots of petroleum products values in the samples.</p>
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<p>Boxplots of metal concentrations in the analyzed sludge: (<b>a</b>) copper concentration range; (<b>b</b>) nickel concentration range; (<b>c</b>) aluminum concentration range.</p>
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26 pages, 1466 KiB  
Article
Leveraging Massive MIMO for Enhanced Energy Efficiency in High-Density IoT Networks
by Byung Moo Lee
Mathematics 2024, 12(22), 3539; https://doi.org/10.3390/math12223539 - 12 Nov 2024
Viewed by 444
Abstract
Maximizing energy efficiency (EE) in massive multiple-input multiple-output (MIMO) systems, while supporting the rapid expansion of Internet of Things (IoT) devices, is a critical challenge. In this paper, we delve into the intricate operations geared toward enhancing EE in such complex environments. To [...] Read more.
Maximizing energy efficiency (EE) in massive multiple-input multiple-output (MIMO) systems, while supporting the rapid expansion of Internet of Things (IoT) devices, is a critical challenge. In this paper, we delve into the intricate operations geared toward enhancing EE in such complex environments. To effectively support a multitude of IoT devices, we adopt a strategy of heavy reference signal (RS) reuse, and in this circumstance, we formulate the EE metrics and their corresponding inverses to determine pivotal operational parameters. These EE-centric parameters encompass factors such as the number of service antennas in the base station (BS), the number of IoT devices, and permissible coverage extents. Our objective is to calibrate these parameters to meet a predefined EE threshold, ensuring optimal system performance. Additionally, we recognize the indispensable role of Peak-to-Average Power Ratio (PAPR) reduction techniques, particularly in multicarrier systems, to further enhance EE. As such, we employ clipping-based PAPR reduction methods to mitigate signal distortions and bolster overall efficiency. Theoretical EE metrics are derived based on formulated signal-to-interference-plus-noise ratios (SINRs), yielding insightful closed-form expressions for the operational parameters. Leveraging two distinct EE metric models, we undertake parameter determinations, accounting for the levels of approximation. Intriguingly, our analysis reveals that even simplified models exhibit remarkable applicability in real-world scenarios, with a minimal margin of error. The results not only underscore the practical applicability of our theoretical constructs but also highlight the potential for significant EE enhancements in massive MIMO systems, thereby contributing to sustainable evolution in the IoT era. Full article
(This article belongs to the Section Engineering Mathematics)
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<p>A block diagram for received signal.</p>
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<p>Relations of Energy Efficiency (EE) and several parameters (<span class="html-italic">M</span>, <span class="html-italic">K</span>, <math display="inline"><semantics> <mi>ν</mi> </semantics></math>); (<b>a</b>) Relation between EE and <span class="html-italic">M</span>, when <math display="inline"><semantics> <mrow> <mi>K</mi> <mo>=</mo> <mn>8400</mn> </mrow> </semantics></math>. (<b>b</b>) Relation between EE and <span class="html-italic">K</span>, <math display="inline"><semantics> <mrow> <mi>M</mi> <mo>=</mo> <mn>500</mn> </mrow> </semantics></math>. (<b>c</b>) Relation between EE and <math display="inline"><semantics> <mi>ν</mi> </semantics></math>, when <math display="inline"><semantics> <mrow> <mi>M</mi> <mo>=</mo> <mn>500</mn> </mrow> </semantics></math> and <math display="inline"><semantics> <mrow> <mi>K</mi> <mo>=</mo> <mn>8400</mn> </mrow> </semantics></math>. (<b>d</b>) Relation between EE and <math display="inline"><semantics> <msub> <mi>p</mi> <mi>u</mi> </msub> </semantics></math>, when <math display="inline"><semantics> <mrow> <mi>M</mi> <mo>=</mo> <mn>500</mn> </mrow> </semantics></math> and <math display="inline"><semantics> <mrow> <mi>K</mi> <mo>=</mo> <mn>8400</mn> </mrow> </semantics></math>.</p>
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<p>Determined parameters and corresponding EE based on the proposed scheme. In each subfigure, “I” represents the determined parameters and “II” indicates the corresponding EE. (<b>a</b>) Relation between <span class="html-italic">M</span> and <math display="inline"><semantics> <mi>ν</mi> </semantics></math>, and corresponding EE, when <math display="inline"><semantics> <mrow> <mi>K</mi> <mo>=</mo> <mn>8400</mn> </mrow> </semantics></math>, <math display="inline"><semantics> <msubsup> <mi mathvariant="sans-serif">EE</mi> <mrow> <mi mathvariant="sans-serif">MR</mi> <mo>,</mo> <mi mathvariant="sans-serif">th</mi> </mrow> <mi mathvariant="monospace">UL</mi> </msubsup> </semantics></math> = 2 Mbps/W. (<b>b</b>) Relation between <span class="html-italic">K</span> and <math display="inline"><semantics> <mi>ν</mi> </semantics></math>, and corresponding EE, when <math display="inline"><semantics> <msubsup> <mi mathvariant="sans-serif">EE</mi> <mrow> <mi mathvariant="sans-serif">MR</mi> <mo>,</mo> <mi mathvariant="sans-serif">th</mi> </mrow> <mi mathvariant="monospace">UL</mi> </msubsup> </semantics></math> = 2 Mbps/W. (<b>c</b>) Relation between <math display="inline"><semantics> <mi>ν</mi> </semantics></math> and <span class="html-italic">M</span>, and corresponding EE, when <math display="inline"><semantics> <mrow> <mi>K</mi> <mo>=</mo> <mn>8400</mn> </mrow> </semantics></math>, <math display="inline"><semantics> <msubsup> <mi mathvariant="sans-serif">EE</mi> <mrow> <mi mathvariant="sans-serif">MR</mi> <mo>,</mo> <mi mathvariant="sans-serif">th</mi> </mrow> <mi mathvariant="monospace">UL</mi> </msubsup> </semantics></math> = 2 Mbps/W. (<b>d</b>) Relation between <math display="inline"><semantics> <mi>ν</mi> </semantics></math> and <span class="html-italic">K</span>, and corresponding EE, when <math display="inline"><semantics> <mrow> <mi>M</mi> <mo>=</mo> <mn>500</mn> </mrow> </semantics></math>, <math display="inline"><semantics> <msubsup> <mi mathvariant="sans-serif">EE</mi> <mrow> <mi mathvariant="sans-serif">MR</mi> <mo>,</mo> <mi mathvariant="sans-serif">th</mi> </mrow> <mi mathvariant="monospace">UL</mi> </msubsup> </semantics></math> = 0.5 Mbps/W. (<b>e</b>) Relation between coverage <math display="inline"><semantics> <mo>Ω</mo> </semantics></math> and <span class="html-italic">M</span>, and corresponding EE, when <math display="inline"><semantics> <mrow> <mi>K</mi> <mo>=</mo> <mn>8400</mn> </mrow> </semantics></math>, <math display="inline"><semantics> <msubsup> <mi mathvariant="sans-serif">EE</mi> <mrow> <mi mathvariant="sans-serif">MR</mi> <mo>,</mo> <mi mathvariant="sans-serif">th</mi> </mrow> <mi mathvariant="monospace">UL</mi> </msubsup> </semantics></math> = 1.5 Mbps/W. (<b>f</b>) Relation between coverage <math display="inline"><semantics> <mo>Ω</mo> </semantics></math> and <span class="html-italic">K</span>, and corresponding EE, when <math display="inline"><semantics> <mrow> <mi>M</mi> <mo>=</mo> <mn>500</mn> </mrow> </semantics></math>, <math display="inline"><semantics> <msubsup> <mi mathvariant="sans-serif">EE</mi> <mrow> <mi mathvariant="sans-serif">MR</mi> <mo>,</mo> <mi mathvariant="sans-serif">th</mi> </mrow> <mi mathvariant="monospace">UL</mi> </msubsup> </semantics></math> = 0.2 Mbps/W.</p>
Full article ">Figure 4
<p>Variations of EE, <math display="inline"><semantics> <mi>ν</mi> </semantics></math>, <math display="inline"><semantics> <msub> <mi>p</mi> <mi>u</mi> </msub> </semantics></math>, <math display="inline"><semantics> <mo>Ω</mo> </semantics></math>, and total CDN. (<b>a</b>) EE with the variation of <span class="html-italic">M</span> and <math display="inline"><semantics> <mi>ν</mi> </semantics></math>, when <span class="html-italic">K</span> = 8400. (<b>b</b>) EE with the variation of <span class="html-italic">K</span> and <math display="inline"><semantics> <mi>ν</mi> </semantics></math>, <span class="html-italic">M</span> = 500. (<b>c</b>) <math display="inline"><semantics> <mi>ν</mi> </semantics></math> based on <span class="html-italic">M</span> and <math display="inline"><semantics> <msub> <mi>p</mi> <mi>u</mi> </msub> </semantics></math>, <span class="html-italic">K</span> = 8400, <math display="inline"><semantics> <msubsup> <mi mathvariant="sans-serif">EE</mi> <mrow> <mi mathvariant="sans-serif">MR</mi> <mo>,</mo> <mi mathvariant="sans-serif">th</mi> </mrow> <mi mathvariant="monospace">UL</mi> </msubsup> </semantics></math> = 2 Mbps/W. (<b>d</b>) <math display="inline"><semantics> <mi>ν</mi> </semantics></math> based on <span class="html-italic">K</span> and <math display="inline"><semantics> <msub> <mi>p</mi> <mi>u</mi> </msub> </semantics></math>, <span class="html-italic">M</span> = 500, <math display="inline"><semantics> <msubsup> <mi mathvariant="sans-serif">EE</mi> <mrow> <mi mathvariant="sans-serif">MR</mi> <mo>,</mo> <mi mathvariant="sans-serif">th</mi> </mrow> <mi mathvariant="monospace">UL</mi> </msubsup> </semantics></math> = 2 Mbps/W. <math display="inline"><semantics> <msubsup> <mi mathvariant="sans-serif">EE</mi> <mrow> <mi mathvariant="sans-serif">MR</mi> <mo>,</mo> <mi mathvariant="sans-serif">th</mi> </mrow> <mi mathvariant="monospace">UL</mi> </msubsup> </semantics></math> = 2 Mbps/W. (<b>e</b>) <math display="inline"><semantics> <msub> <mi>p</mi> <mi>u</mi> </msub> </semantics></math> based on <span class="html-italic">M</span> and <math display="inline"><semantics> <mi>ν</mi> </semantics></math>, <math display="inline"><semantics> <msubsup> <mi mathvariant="sans-serif">EE</mi> <mrow> <mi mathvariant="sans-serif">MR</mi> <mo>,</mo> <mi mathvariant="sans-serif">th</mi> </mrow> <mi mathvariant="monospace">UL</mi> </msubsup> </semantics></math> = 1.5 Mbps/W. (<b>f</b>) <math display="inline"><semantics> <msub> <mi>p</mi> <mi>u</mi> </msub> </semantics></math> based on <span class="html-italic">K</span> and <math display="inline"><semantics> <mi>ν</mi> </semantics></math>, <math display="inline"><semantics> <msubsup> <mi mathvariant="sans-serif">EE</mi> <mrow> <mi mathvariant="sans-serif">MR</mi> <mo>,</mo> <mi mathvariant="sans-serif">th</mi> </mrow> <mi mathvariant="monospace">UL</mi> </msubsup> </semantics></math> = 1.5 Mbps/W. (<b>g</b>) Coverage <math display="inline"><semantics> <mo>Ω</mo> </semantics></math> based on <span class="html-italic">K</span> and <span class="html-italic">M</span>, <math display="inline"><semantics> <msubsup> <mi mathvariant="sans-serif">EE</mi> <mrow> <mi mathvariant="sans-serif">MR</mi> <mo>,</mo> <mi mathvariant="sans-serif">th</mi> </mrow> <mi mathvariant="monospace">UL</mi> </msubsup> </semantics></math> = 0.2 Mbps/W. (<b>h</b>) Total CDN with variation of <span class="html-italic">K</span> and <span class="html-italic">M</span>, when <math display="inline"><semantics> <mi>ν</mi> </semantics></math> = 5 dB. (<b>i</b>) Total CDN with variation of <span class="html-italic">M</span> and <math display="inline"><semantics> <mi>ν</mi> </semantics></math>, when <math display="inline"><semantics> <mrow> <mi>K</mi> <mo>=</mo> <mn>8400</mn> </mrow> </semantics></math>.</p>
Full article ">Figure 5
<p>CDF of EE.</p>
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