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Search Results (1,017)

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2 pages, 121 KiB  
Abstract
Potential of Lignocellulosic Agro-Waste to Produce Value-Added Products
by Uloma Onyeka, Egwu Kalu and Damaris Okafor
Proceedings 2023, 91(1), 127; https://doi.org/10.3390/proceedings2023091127 - 22 Jan 2024
Viewed by 591
Abstract
This work focused on the effect of combustion on the yield, composition, and strength of food-grade bio- alkali from lignocellulosic agro-waste. Seven lignocellulosic types of agro-waste, including plantain stalk, plantain peel (green and ripe), empty palm bunch, palm fiber, coconut fiber, and cocoa [...] Read more.
This work focused on the effect of combustion on the yield, composition, and strength of food-grade bio- alkali from lignocellulosic agro-waste. Seven lignocellulosic types of agro-waste, including plantain stalk, plantain peel (green and ripe), empty palm bunch, palm fiber, coconut fiber, and cocoa pod were sun-dried and combusted using two methods: open-air combustion (OAC) and muffle furnace combustion (MFC). Ash and potash yield from the two methods of combustion were determined using simple proportion calculations. A two-stage hydrothermal extraction process was carried out on the ash using a deionized water ratio of 1:10 for food-grade bio-alkali, and the leachates were evaluated for pH, alkalinity, and metallic ion contents using standard analytical methods. The data obtained were statistically analyzed via a two-way ANOVA. The OAC samples had a higher ash content range (8.24–18.6%) compared to MFC samples (7.37–9.89%). Potash yield (%) is both biomass and combustion-method dependent, with MFC having a higher average yield (3.05%) than OAC (2.35%). The pH of the leachates for all samples ranged from 10.3 to 12.0. All the agro-waste exhibited a similar pattern in the order of magnitude of the metals of which they were composed (K > Mg > Ca > Zn > Na). For the minerals, PO4 was highest (193.1 g/L) in plantain stalk, and KOH and K2CO3 were least (10.0 g/L) in coconut fiber, while the highest alkalinity was obtained in ripe plantain peel (62.1 mg/L). The yield and quality of bio-alkali produced were influenced by the combustion method and source of biomass. The bio-alkali from the different biomass types tested can be used as sources of food-grade emulsifiers due to their high nature of alkalinity. This signifies zero waste and is also a boost to the circular economy. The average alkalinity studied under MFC was 33.6 mg/L and for OAC was 27.3 mg/L, suggesting that MFC is a more promising approach. Worthy of exploration is the significant high content (19.3 mg/L) of chlorine in plantain stalk. Full article
(This article belongs to the Proceedings of The 14th European Nutrition Conference FENS 2023)
30 pages, 14011 KiB  
Article
Fluid Evolution of Greisens from Krupka Sn-W Ore District, Bohemian Massif (Czech Republic)
by Michaela Krejčí Kotlánová, Zdeněk Dolníček, Miloš René, Walter Prochaska, Jana Ulmanová, Jaroslav Kapusta, Vlastimil Mašek and Kamil Kropáč
Minerals 2024, 14(1), 86; https://doi.org/10.3390/min14010086 - 11 Jan 2024
Cited by 1 | Viewed by 1606
Abstract
The Sn-W ore deposits in the Krupka surroundings are associated with greisens, which occur in the upper parts of Late Variscan granitoid intrusions. Fluid inclusions were studied in samples of quartz, cassiterite, apatite, fluorite, and topaz in greisenized granites, greisens, and hydrothermal veins [...] Read more.
The Sn-W ore deposits in the Krupka surroundings are associated with greisens, which occur in the upper parts of Late Variscan granitoid intrusions. Fluid inclusions were studied in samples of quartz, cassiterite, apatite, fluorite, and topaz in greisenized granites, greisens, and hydrothermal veins with Sn-W mineralization. The greisenization process took place at temperatures 370–490 °C and pressures 155–371 bars, and associated fluids had predominantly low salinity and a low gas (CO2, N2 and CH4) content. The post-greisenization stage was connected with the formation of (i) low-salinity (0–8 wt. % NaCl eq.) fluid inclusions with homogenization temperatures <120–295 °C and (ii) high-salinity (18 to >35 wt. % NaCl eq.) fluid inclusions with homogenization temperatures 140–370 °C, often containing trapped crystals of quartz, topaz, and sulfides, or daughter crystals of salts and carbonates, which were identified by microthermometric measurements, electron microprobe analysis, and Raman spectroscopy. Analyses of fluid inclusion leachates have shown that Na and Ca chlorides predominate in fluids. According to hydrogen stable isotopes, the source of greisenizing and post-greisenizing fluids was not only magmatogenic but also meteoric water or fluids derived from sedimentary rocks. Full article
(This article belongs to the Special Issue Geochemistry and Genesis of Hydrothermal Ore Deposits)
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Graphical abstract

Graphical abstract
Full article ">Figure 1
<p>Geological map of the Krupka ore district with the location of the main ore fields and abandoned mine workings (modified after [<a href="#B21-minerals-14-00086" class="html-bibr">21</a>]) and the WNW–ESE geological cross-section through the Krupka surroundings (modified after [<a href="#B22-minerals-14-00086" class="html-bibr">22</a>]).</p>
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<p>The texture and mineral composition of studied samples from the Krupka ore district. (<b>a</b>) Greisen sample with molybdenite from Prokop Stock, sample KR-11; (<b>b1</b>) Quartz greisen with hydrothermal vein with a cavity filled with fluorite, sample KR-12; (<b>b2</b>) Detail of cavity with fluorite crystals; (<b>c</b>) Topaz on greisen sample from Prokop Stock; sample JM-1; (<b>d</b>) Greisen sample with cassiterite from Knötel area, sample KR-10; (<b>e1</b>) Violet fluorite and light blue apatite on greisen sample from adit Martin, sample MA-3; (<b>e2</b>) Detail of apatite from (<b>e</b>); (<b>f</b>) Greisen sample with an abundant amount of sulfides, predominantly chalcopyrite from dump material from adit Sedmi spáčů, Knötel area, sample KR-3; (<b>g</b>) Sample of greisenized granite with dark greisen zones around quartz vein from Knötel area, adit Preisselberg II—sample PRK-1; (<b>h</b>) Perfectly limited crystal of quartz from Steinknochen area, Martin adit—sample KNM-3.</p>
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<p>XRD records of clay minerals from greisen sample KR-4 (black spectrum) and hydrothermal vein sample KR-12 (red spectrum) from Knötel area; dck—dickite, ill—illite, qtz—quartz.</p>
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<p>Mineral assemblages and texture of the samples. (<b>a</b>) Greisen from Preisselberg (sample PRK-1) cut by quartz vein (Qtz), polarized light, XPL; (<b>b</b>) Grain of cassiterite (Cst) with zonal structure and zinnwaldite (Znw) fan-like crystals in greisenized granite from Preisselberg (PRK-1), polarized light, XPL; (<b>c</b>) Zonal tabular crystals of micas corresponding to muscovite (Msc) and zinnwaldite (Znw) enclosed in quartz (Qtz) from greisen (PRK-1), BSE image; (<b>d</b>) Wolframite grains enclosed in cassiterite, BSE image; (<b>e</b>) Cassiterite (Cst) in mica interlayers and in association with apatite (Ap) from greisen from Knötel–Prokop Stock (KNM-2), BSE image; (<b>f</b>) Zonal TiO<sub>2</sub> phase in association with quartz and cassiterite (Cst) in greisen from Knötel–Prokop Stock (KNM-2), BSE image.</p>
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<p>Appearance of fluid inclusions in minerals from the Krupka ore district in polarized light (PPL) at room temperature: (<b>a</b>) Primary inclusion from topaz from greisen sample KNM-2; (<b>b</b>) Vapor-rich negative crystal-shaped primary fluid inclusions from quartz from greisen sample KR-11 from Knötel; (<b>c</b>) Solitary primary fluid inclusion from quartz from vein sample KNM-3; (<b>d</b>) Pseudosecondary inclusion from fluorite from vein sample KR-12; (<b>e</b>) Short trail of pseudosecondary inclusions from quartz from greisen with variable LVR, sample KR-12; (<b>f</b>) Secondary inclusion from quartz from greisenized granite affected by necking-down, sample PRK-1; (<b>g</b>) Group of secondary liquid and liquid-vapor fluid inclusions from greisen, sample KR-12; (<b>h</b>) Trail of secondary inclusions from vein quartz; sample PRK-1. Scale bar is 20 µm for all microphotographs.</p>
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<p>Appearance of multiphase pseudosecondary/secondary fluid inclusions with solid phases in quartz from greisen sample KR-12 (<b>a</b>–<b>d</b>) and KR-11 (<b>e</b>–<b>h</b>) from Prokop Stock, trail of multiphase SFI3 inclusions from quartz from vein sample KNM-3 (younger generation of SFI3); (<b>i</b>) from Steinknochen (Martin adit) and cassiterite from greisenized granite (sample PRK-1) from Preisselberg (<b>j</b>) under the microscope in polarized light at room temperature (PPL), H—halite; fluid inclusions in quartz from greisen sample KR-12 in BSE: (<b>k</b>) Group of opened fluid inclusions in quartz from greisen sample KR-12 from Prokop Stock with grains of quartz (QTZ); (<b>l</b>) Fluid inclusion in quartz from greisen sample KR-12 from Prokop Stock encloses crystal of topaz (TPZ); scale bar is 20 µm for all microphotographs.</p>
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<p>Raman spectrum of a solid carbonate enclosed in a multiphase SFI3 from vein quartz from Krupka (sample KMN-3). The size of the studied inclusion is 27 µm.</p>
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<p>Histograms of homogenization temperatures and ice melting temperatures of fluid inclusions from Krupka, G—greisens, GG—greisenized granites, V—veins: (<b>a</b>) Homogenization temperatures of primary inclusions, bars indicate the ranges for individual modes of homogenization; (<b>b</b>) Ice melting temperatures of primary inclusions; (<b>c</b>) Homogenization temperatures of pseudosecondary and secondary fluid inclusions; (<b>d</b>) Ice melting temperatures of pseudosecondary and secondary inclusions.</p>
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<p>Plot Th vs. Tds<sub>H</sub> vs. salinity (model) after [<a href="#B53-minerals-14-00086" class="html-bibr">53</a>] with data points of SFI3 from the Krupka ore district.</p>
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<p>Example of phase transitions during heating of a PSFI/SFI3 fluid inclusion from vein quartz from sample KNM-3 (Lukáš vein, Martin adit).</p>
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<p>Raman spectrum of gaseous phase enclosed in a primary fluid inclusion from quartz in greisen from Krupka (KR-12).</p>
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<p>Plot of temperature of homogenization vs. ice melting temperature for fluid inclusions from Krupka and comparison with localities Vykmanov [<a href="#B16-minerals-14-00086" class="html-bibr">16</a>], Horní Slavkov–Hub Stock [<a href="#B17-minerals-14-00086" class="html-bibr">17</a>], and Zinnwald [<a href="#B54-minerals-14-00086" class="html-bibr">54</a>].</p>
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<p>Results of Raman analyses of non-aqueous phases of fluid inclusions from Krupka in ternary plot CO<sub>2</sub>-CH<sub>4</sub>-N<sub>2</sub> and comparison with samples from other localities in the Bohemian Massif, W-mineralization from Jablonec nad Nisou [<a href="#B56-minerals-14-00086" class="html-bibr">56</a>] and greisens from Hub Stock [<a href="#B17-minerals-14-00086" class="html-bibr">17</a>].</p>
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<p>Pressure and temperature conditions of trapping of PFI connected with process of greisenization from Krupka and comparison with other localities, Horní Slavkov–Hub Stock [<a href="#B17-minerals-14-00086" class="html-bibr">17</a>], Boží Dar, Vykmanov, Přebuz [<a href="#B16-minerals-14-00086" class="html-bibr">16</a>] and trapping of brines from Krupka [<a href="#B15-minerals-14-00086" class="html-bibr">15</a>]. Diagram modified after [<a href="#B58-minerals-14-00086" class="html-bibr">58</a>].</p>
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<p>Ternary diagrams NO<sub>3</sub><sup>−</sup>-SO<sub>4</sub><sup>2−</sup>-Cl<sup>−</sup> and K<sup>+</sup>-(Na<sup>+</sup>+Li<sup>+</sup>)-(Ca<sup>2+</sup>+Mg<sup>2+</sup>) in leachates of fluid inclusions from Krupka and comparison with leachates from Horní Slavkov–Hub Stock [<a href="#B17-minerals-14-00086" class="html-bibr">17</a>] and post-Variscan hydrothermal mineralization from the Bohemian Massif [<a href="#B63-minerals-14-00086" class="html-bibr">63</a>].</p>
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<p>I/Cl vs. Br/Cl plot for leachates of fluid inclusions from Krupka and comparison with other localities—Hub Stock [<a href="#B17-minerals-14-00086" class="html-bibr">17</a>], high-salinity post-Variscan fluids of Bohemian Massif [<a href="#B63-minerals-14-00086" class="html-bibr">63</a>,<a href="#B64-minerals-14-00086" class="html-bibr">64</a>] and various other sources—sea water, mantle; SET—seawater evaporation trajectory. Plot modified after [<a href="#B17-minerals-14-00086" class="html-bibr">17</a>].</p>
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<p>The calculated δD values of parent fluids from samples from Krupka ore district and their comparison with geologically important reservoirs [<a href="#B68-minerals-14-00086" class="html-bibr">68</a>], granites from Horní Slavkov–Hub Stock [<a href="#B17-minerals-14-00086" class="html-bibr">17</a>] and Cínovec [<a href="#B14-minerals-14-00086" class="html-bibr">14</a>], greisens from Iberian Central system [<a href="#B70-minerals-14-00086" class="html-bibr">70</a>], greisen cassiterite mineralization from Uljin Area [<a href="#B71-minerals-14-00086" class="html-bibr">71</a>], greisens from New Ross area in Canada [<a href="#B72-minerals-14-00086" class="html-bibr">72</a>], Sn-W mineralization, Mawchi, Myanmar [<a href="#B73-minerals-14-00086" class="html-bibr">73</a>], and unpublished data by M. René for topaz-albite granites of the Bohemian Massif.</p>
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<p>Simplified model of fluid evolution in the Knötel Stock.</p>
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9 pages, 391 KiB  
Communication
Effects of Glomus fasciculatum, Azotobacter chroococcum and Vermicompost Leachate on the Production and Quality of Tomato Fruit
by Alejandro Alarcón-Zayas, Luis Guillermo Hernández-Montiel, Diana Medina-Hernández, Edgar Omar Rueda-Puente, Wilson Geobel Ceiro-Catasú and Ramón Jaime Holguín-Peña
Microbiol. Res. 2024, 15(1), 187-195; https://doi.org/10.3390/microbiolres15010013 - 11 Jan 2024
Viewed by 1085
Abstract
Arbuscular mycorrhizal fungi, plant-growth-promoting bacteria (PGPB) and vermicompost constitute important environmental and economic resources for improving the production and quality of tomato fruits. The present research aims to determine the single and combined effect of Glomus fasciculatum (Gf) fungus, Azotobacter chroococcum (Azot), PGPB [...] Read more.
Arbuscular mycorrhizal fungi, plant-growth-promoting bacteria (PGPB) and vermicompost constitute important environmental and economic resources for improving the production and quality of tomato fruits. The present research aims to determine the single and combined effect of Glomus fasciculatum (Gf) fungus, Azotobacter chroococcum (Azot), PGPB and vermicompost leachate (VL) organic fertilizer on the yield and quality of tomato fruit. Thus, an open-field experiment was established with seven treatments, a control and three replicates. Total soluble solids, vitamin C, acidity, fruit mass and fruit diameter were evaluated as fruit quality variables; the yield was recorded and estimated in tons per hectare−1. The results showed that Gf, Azot and VL were effective in promoting tomato yield and fruit quality. As a trend, the triple combination (Gf + Azot + VL) evidently obtained the highest values of total soluble solids, vitamin C and fruit acidity. The range of improvement concerning the fruit size was 66.6% (single treatment) compared to 78.5% (triple combination). The maximum yield of 54.5 t/ha−1 was recorded for the Gf + Azot + VL combination. Therefore, G. fasciculatum, A. chroococcum and VL are considered useful as organic alternatives for open-field tomato biofertilization programs in tropical countries. Full article
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Figure 1
<p>Effect of <span class="html-italic">Glomus fasciculatum</span> (Gf), <span class="html-italic">Azotobacer chroococcum</span> (Azot) and vermicompost leachate (VL) on dry mass (DM) of tomato fruit. Vertical bars ± standard error (SE) are shown; the different letters differed significantly (Tukey’s test, <span class="html-italic">p</span> &lt; 0.05).</p>
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<p>Effect of <span class="html-italic">Glomus fasciculatum</span> (Gf), <span class="html-italic">Azotobacter chroococcum</span> (Azot) and vermicompost leachate (VL) on total soluble solids (TSS) in tomato fruit. Vertical bars ± standard error (SE) are shown; the different letters differed significantly (Tukey’s test, <span class="html-italic">p</span> &lt; 0.05).</p>
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<p>Effect of <span class="html-italic">Glomus fasciculatum</span> (Gf), <span class="html-italic">Azotobacer chroococcum</span> (Azot) and vermicompost leachate (VL) on tomato yield. Vertical bars ± standard error (SE) are shown; the different letters differed significantly (Tukey’s test, <span class="html-italic">p</span> &lt; 0.05).</p>
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<p>The vitamin C content of tomato fruit was assessed by applying <span class="html-italic">Glomus fasciculatum</span> (Gf), <span class="html-italic">Azotobacte chroococcum</span> (Azot) and vermicompost leachate (VL), either alone or combined. Vertical bars ± standard error (SE) are shown; the different letters differed significantly (Tukey’s test, <span class="html-italic">p</span> &lt; 0.05).</p>
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28 pages, 3920 KiB  
Article
Assessment of Phytotoxicity in Untreated and Electrochemically Treated Leachates through the Analysis of Early Seed Growth and Inductively Coupled Plasma-Optical Emission Spectroscopy Characterization
by Alfredo Martínez-Cruz and María Neftalí Rojas-Valencia
Horticulturae 2024, 10(1), 67; https://doi.org/10.3390/horticulturae10010067 - 9 Jan 2024
Viewed by 1605
Abstract
The treatment of stabilized leachates with high refractory organic matter content, which are over 10 years old, presents a challenge. This study explored the potential of electro-coagulation (EC) and electro-oxidation (EO) treatment systems to address this issue. The objective of this study was [...] Read more.
The treatment of stabilized leachates with high refractory organic matter content, which are over 10 years old, presents a challenge. This study explored the potential of electro-coagulation (EC) and electro-oxidation (EO) treatment systems to address this issue. The objective of this study was to investigate the phytotoxicity of the proposed treatment system on seed growth and examine possible relationships between phytotoxicity results and the characterization of leachates, effluents, soil, and radicles. Phytotoxicity tests were conducted on seeds of Lactuca sativa, Cucumis sativus, and Phaseolus vulgaris, using Inductively Coupled Plasma-Optical analysis. The evolution of organic matter was monitored by fractionating the chemical oxygen demand (COD) and humic substances. The biodegradability index increased from 0.094 in raw leachate to 0.26 and 0.48 with EC and EO, respectively. Removal rates of 82%, 86%, 99%, and 81% were achieved for COD, dissolved organic carbon, color, and ammoniacal nitrogen, respectively. The biodegradable COD increased from 26% in raw leachate to 39% in the EC process and 58% in the EO process effluent. The proposed treatment system successfully broke the aromatic structures of the humic substances present in the raw leachate, thereby increasing the content of biodegradable material. Phytotoxicity tests revealed that the proposed treatment system significantly reduced the phytotoxicity of the generated effluents. Full article
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Figure 1
<p>Diagram of the methodology developed in the project.</p>
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<p>Study area. Bordo Poniente landfill (Google Maps).</p>
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<p>Experimental setup used in the experimentation of this project.</p>
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<p>Germination tray used in the phytotoxicity experiments.</p>
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<p>Growth inhibition through radicle length in toxicity tests.</p>
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<p>Growth inhibition through biomass gained in toxicity tests.</p>
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<p>Germination index in toxicity tests.</p>
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15 pages, 2261 KiB  
Article
Microbiome Structure of Activated Sludge after Adaptation to Landfill Leachate Treatment in a Lab-Scale Sequencing Batch Reactor
by Mihaela Kirilova, Ivaylo Yotinov, Yovana Todorova, Nora Dinova, Stilyana Lincheva, Irina Schneider and Yana Topalova
Processes 2024, 12(1), 159; https://doi.org/10.3390/pr12010159 - 9 Jan 2024
Cited by 1 | Viewed by 1483
Abstract
During adaptation to waters that are rich in xenobiotics, biological systems pass through multiple stages. The first one is related to the restructuring of communities, pronounced destruction of the structure, and multiplication of active biodegradants. The purpose of the present research was to [...] Read more.
During adaptation to waters that are rich in xenobiotics, biological systems pass through multiple stages. The first one is related to the restructuring of communities, pronounced destruction of the structure, and multiplication of active biodegradants. The purpose of the present research was to describe the microbiome restructuring that occurs during the adaptation stage in landfill leachate treatment. In a model SBR (sequencing batch reactor), a 21-day purification process of landfill leachate was simulated. Wastewater was fed in increasing concentrations. When undiluted leachate entered, the activated sludge structure disintegrated (Sludge Volume Index—4.6 mL/g). The Chemical Oxygen Demand and ammonium nitrogen concentration remained at high values in the influent (2321.11 mgO2/L and 573.20 mg/L, respectively). A significant amount of free-swimming cells was found, and the number of aerobic heterotrophs and bacteria of the genera Pseudomonas and Acinetobacter increased by up to 125 times. The Azoarcus-Thauera cluster (27%) and Pseudomonas spp. (16%) were registered as the main bacterial groups in the activated sludge. In the changed structure of the microbial community, Gammaproteobacteria, family Rhizobiaceae, class Saccharimonadia were predominantly represented. Among the suspended bacteria, Microbactericeae and Burkholderiaceae, which are known for their ability to degrade xenobiotics, were present in larger quantities. The enzymological analysis demonstrated that the ortho-pathway of cleavage of aromatic structures was active in the community. The described changes in the leachate-purifying microbial community appear to be destructive at the technological level. At the microbiological level, however, trends of initial adaptation were clearly outlined, which, if continued, could provide a highly efficient biodegradation community. Full article
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<p>Experimental design.</p>
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<p>Number of the bacteria from the key groups, determined by plate counting techniques.</p>
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<p>Digital image analysis of FISH images of samples at the four control points during the experiments.</p>
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<p>Metagenomic analysis of the activated sludge at the end of the model SBR treatment of landfill leachate (21st day).</p>
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<p>Metagenomic analysis of the free-swimming bacteria in the activated sludge at the end of the model SBR treatment of landfill leachate (21st day).</p>
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<p>Activity of the key detoxifying enzymes (C12DO—catechol-1,2-dioxygenase; C23DO—catechol-2,3-dioxygenase; P34DO—protocatechuate-3,4-dioxygenase; TDA—total dehydrogenase activity) and the remaining pollutants which was measured as COD.</p>
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22 pages, 2300 KiB  
Article
The Impact of Soil and Water Pollutants Released from Poultry Farming on the Growth and Development of Two Plant Species
by Magdalena Krupka, Ewa Olkowska, Agnieszka Klimkowicz-Pawlas, Leszek Łęczyński, Maciej Tankiewicz, Dariusz J. Michalczyk, Lidia Wolska and Agnieszka I. Piotrowicz-Cieślak
Agriculture 2024, 14(1), 87; https://doi.org/10.3390/agriculture14010087 - 31 Dec 2023
Cited by 2 | Viewed by 2806
Abstract
Intensive poultry production may result in substantial emissions of pollutants into the environment, including pharmaceuticals and other chemicals used in poultry farming. The objective of this study was to verify the presence of ciprofloxacin, enrofloxacin, carbamazepine, metoclopramide, trimethoprim, diflufenican, flufenacet, and p,p′-DDE in [...] Read more.
Intensive poultry production may result in substantial emissions of pollutants into the environment, including pharmaceuticals and other chemicals used in poultry farming. The objective of this study was to verify the presence of ciprofloxacin, enrofloxacin, carbamazepine, metoclopramide, trimethoprim, diflufenican, flufenacet, and p,p′-DDE in soil and water in the immediate vicinity of a poultry manure heap. The influence of soil contaminants on the growth and selected physiological parameters of seed peas and common duckweed (as indicator plants) was tested. It has been proven that the cultivation of pea plants on soil coming from the close proximity of a heap of manure results in a deterioration of both morphological parameters (root length, shoot length) and physiological parameters (chlorophyll absorption, aminolevulinic acid dehydrogenase (ALAD) activity, aminolevulinic acid (ALA) content, lipid peroxidation, mitochondrial damage or production of HSP70 proteins). Similarly, water extracts from cultivated soils had a significant effect on duckweed, and it was found that contaminant leachates are indeed detectable in soil, groundwater, and deep water. Special attention should, therefore, be paid to the location, methods of storage, and use of poultry fertilizer. Full article
(This article belongs to the Special Issue The Influence of Environmental Factors on Farming Animals)
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Figure 1
<p>General appearance of peas: 1—pea grown on soil regularly fertilized with manure, 2—pea grown on soil taken from the vicinity of a manure heap, 3—pea grown on horticultural perlite-controland morphological parameters (<b>A</b>) shoot length [cm], (<b>B</b>) length of the main root [cm], (<b>C</b>) number of side roots, (<b>D</b>) area of the second leaf [cm<sup>2</sup>]. 1 (yellow column)—pea grown on soil regularly fertilized with manure, 2 (red column)—pea grown on soil taken from the vicinity of a manure heap, 3 (green column)—pea grown on horticultural perlite—control. Means marked with different letters differ significantly (<span class="html-italic">p</span> ≤ 0.05) between groups (ANOVA, Tukey HSD test).</p>
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<p>ALAD activity [nmol PGB/min/mg protein] (<b>A</b>) and ALA content [nmol × one plant<sup>−1</sup>] (<b>B</b>) in peas grown on soil regularly fertilized with manure—1 (yellow column); collected from the vicinity of manure heaps—2 (red column) and the horticultural perlite—3 (green column). Means marked with different letters differ significantly (<span class="html-italic">p</span> ≤ 0.05) between groups (ANOVA, Tukey HSD test).</p>
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<p>Biochemical parameters (<b>A</b>) concentration of MDA [nmol × mL<sup>−1</sup> × one plant<sup>−1</sup>], (<b>B</b>) damage to mitochondria [%], (<b>C</b>) concentration of HSP70 proteins [ng × mL × one plant<sup>−1</sup>]) of pea growing on soil regularly fertilized with manure—1 (yellow column), collected from the vicinity of manure heaps—2 (red column) and on horticultural perlite—3 (green column; plants grown in perlite did not exhibit any symptoms of mitochondrial damage). Means marked with different letters differ significantly (<span class="html-italic">p</span> ≤ 0.05) between groups (ANOVA, Tukey HSD test).</p>
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<p>Morphological parameters (<b>A</b>) number of plants, (<b>B</b>) area of fronds [mm<sup>2</sup>], (<b>C</b>) root length [mm]; 1 (yellow column)—duckweed cultivated on the filtrate of soil regularly fertilized with manure, 2 (red column)—duckweed grown on filtrate of soil taken from the vicinity of the manure heap, 3 (green column)—duckweed grown on MS medium. Means marked with different letters differ significantly (<span class="html-italic">p</span> ≤ 0.05) between groups (ANOVA, Tukey HSD test).</p>
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<p>General appearance of duckweed: 1—duckweed grown on the filtrate from soil regularly fertilized with manure, 2—duckweed growing on the filtrate of soil taken from the vicinity of manure heap, 3—duckweed grown on MS medium) and ALAD activity [nmol PGB × min × mg protein <sup>−1</sup>] (<b>A</b>) and ALA content [nmol × 100 plants<sup>−1</sup>] (<b>B</b>) in duckweed growing on the filtrate of soil regularly fertilized with manure—1 (yellow column), collected from the vicinity of manure heap—2 (red column) and on the medium of MS—3 (green column). Means marked with different letters differ significantly (<span class="html-italic">p</span> ≤ 0.05) between groups (ANOVA, Tukey HSD test).</p>
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<p>Biochemical parameters (<b>A</b>) concentration of MDA [nmol × mL<sup>−1</sup> × 100 plants<sup>−1</sup>], (<b>B</b>) damage to mitochondria [%], (<b>C</b>) concentration of HSP70 proteins [ng × mL<sup>−1</sup> × 100 plants<sup>−1</sup>]) of duckweed <span class="html-italic">Lemna minor</span> L. growing on the filtrate of soil regularly fertilized with manure—1 (yellow column), collected from the vicinity of manure heap—2 (red column) and on perlite rinsed with the minerals of 50% MS medium—3 (green column). Duckweed grown on perlite with minerals of 50% MS medium did not exhibit any symptoms of mitochondrial damage. Means marked with different letters differ significantly (<span class="html-italic">p</span> ≤ 0.05) between groups (ANOVA, Tukey HSD test).</p>
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<p>Map 1. The map of sampling locations. The colors are different because various plants are growing in neighboring fields. Dark green points next to the manure heap correspond to a grove.</p>
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7 pages, 3034 KiB  
Proceeding Paper
Electric Arc Furnace Dust Vitrification via Soda Lime Recycled Glass
by Andronikos Maris, Dimitra Ioannidou, Ilias Sammas, Stavros Deligiannis and Petros E. Tsakiridis
Mater. Proc. 2023, 15(1), 69; https://doi.org/10.3390/materproc2023015069 - 27 Dec 2023
Viewed by 582
Abstract
The present research work focuses on the characterization and leachability evaluation of electric arc furnace dust (EAFD) and its vitreous outgrowths produced during vitrification with soda lime recycled glass (SLRG). EAFD is a hazardous industrial waste generated in the collection of particulate material [...] Read more.
The present research work focuses on the characterization and leachability evaluation of electric arc furnace dust (EAFD) and its vitreous outgrowths produced during vitrification with soda lime recycled glass (SLRG). EAFD is a hazardous industrial waste generated in the collection of particulate material during the steelmaking process via an electric arc furnace. Glasses of various syntheses were obtained during EAFD vitrification with various amounts of silica scrap (50, 60 and 70 wt%). The characterization of the as-received dust was carried out by using granulometry analysis, chemical analysis, X-ray diffraction (XRD), and scanning electron microscopy (SEM), in conjunction with Energy Dispersive X-ray Spectroscopy (EDS). The produced glasses during vitrification were studied by means of chemical and mineralogical analysis, whereas their microstructure in polished sections was examined by SEM/EDS. Their behavior during leaching was determined by the EN 12457-2 compliance leaching test and according to the results, the trace elements detected in the leachates were well below the corresponding regulatory limits. Full article
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<p>Particle size distributions of the EAFD and raw mixtures after grinding.</p>
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<p>Mineralogical phases of the EAFD, SLRG and raw mixtures.</p>
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<p>SEM micrographs of the as-received EFAD.</p>
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<p>Mineralogical phases of the produced vitreous outgrowths.</p>
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<p>Backscattered electron micrographs of vitreous outgrowths polished sections. a: amorphous glass, b: spinel (Fe,Mn,Zn)(Fe,Mn)<sub>2</sub>O<sub>4</sub>, c: augite (Ca(Mg,Fe,Al)(Si,Al)<sub>2</sub>O<sub>6</sub>); d: diopside (CaMg(SiO<sub>3</sub>)<sub>2</sub>.</p>
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16 pages, 2709 KiB  
Article
Biochar-Assisted Phytoremediation Potential of Sewage Sludge Contaminated Soil
by Olga Anne, Ieva Mockevičienė, Danutė Karčauskienė, Regina Repšienė, Gintaras Šiaudinis, Karolina Barčauskaitė and Greta Žilė
Sustainability 2024, 16(1), 183; https://doi.org/10.3390/su16010183 - 24 Dec 2023
Cited by 2 | Viewed by 1636
Abstract
Environmental pollution caused by increasing levels of heavy metals (HM) is a pressing problem throughout the world. Phytoremediation is considered a prospective remediation approach for HM-contaminated soil, but more research is required to enhance remediation efficiency. Biochar is a promising bio-residue material that [...] Read more.
Environmental pollution caused by increasing levels of heavy metals (HM) is a pressing problem throughout the world. Phytoremediation is considered a prospective remediation approach for HM-contaminated soil, but more research is required to enhance remediation efficiency. Biochar is a promising bio-residue material that can be used for the sustainable remediation of heavy metal-contaminated soil. In this study, a pot experiment was conducted to investigate the effects of biochar from different bio-substrates (digestate, waste of biodiesel production from rapeseed, corn stalk) on HM (Cr, Cd, Cu, Ni, Pb, and Zn) accumulation in buckwheat and white mustard cultivated in sewage sludge-contaminated soil. The total amount of HM in soil, plant above- and below-ground biomass, leachate, and bioconcentration and translocation factors were studied to explore the mechanism of how the different bio-substrates’ biochar affects HM accumulation in selected plants. It was observed that rapeseed biochar showed the greatest significant effect in reducing the HM content in soil, plant biomass, and lysimetric water. Meanwhile, the incorporation of digestate biochar significantly increased the HM content in all the soil-plant systems and affected the HM leaching from the soil. The concentration of HM in the leachate decreased from 2.5 to 10 times. It was determined that phytostabilization is the core process of HM accumulation in buckwheat, in contrast to mustard, where the mechanism is phytoextraction. This study confirmed that biochar addition enhances the phytoremediation efficiency in soil, which can potentially improve the development of ecofriendly in-situ bioremediation technology for HM-contaminated sites. Full article
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<p>The bio-substrates and biochars are: (<b>a</b>) digestate; (<b>b</b>) waste of biodiesel production from rapeseed; and (<b>c</b>) corn stalks, where on the left side of pictures—bio—substrate and on the right side—prepared biochar.</p>
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<p>Preparation of the pots’ experiment: preparation of substrate, soil compaction, pots preparation for planting, sowing (from <b>left</b> to <b>right</b>).</p>
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<p>Scheme of the pots’ experiment. Note: Control—soil without any amendments; SS—sewage sludge; RB<sub>450</sub>—rapeseed biochar at 450 °C; RB<sub>700</sub>—rapeseed biochar at 700 °C; DB<sub>450</sub>—digestate biochar at 450 °C; DB<sub>700</sub>—digestate biochar at 700 °C; CB<sub>450 and 700</sub>—corn stalk biochar at 450 °C; and 700 °C.</p>
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<p>The concentration of heavy metals (mean ± standard deviation) in the soil after growing buckwheat (<b>A</b>) and white mustard (<b>B</b>). Note: SS—sewage sludge; SS + RB<sub>450</sub>—sewage sludge + rapeseed biochar at 450 °C; SS + RB<sub>700</sub>—sewage sludge + rapeseed biochar at 700 °C; SS + DB<sub>450</sub>—sewage sludge + digestate biochar at 450 °C; SS + DB<sub>700</sub>—sewage sludge + digestate biochar at 700 °C; SS + CB<sub>450 and 700</sub>—sewage sludge + corn stalk biochar at 450 °C; and 700 °C.</p>
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<p>The heavy metal concentration (mean ± standard deviation) in buckwheat (<b>A</b>) and white mustard (<b>B</b>) roots after biochar incorporation. Note: SS—sewage sludge; SS + RB<sub>450</sub>—sewage sludge + rapeseed biochar at 450 °C; SS + RB<sub>700</sub>—sewage sludge + rapeseed biochar at 700 °C; SS + DB<sub>450</sub>—sewage sludge + digestate biochar at 450 °C; SS + DB<sub>700</sub>—sewage sludge + digestate biochar at 700 °C; SS + CB<sub>450 and 700</sub>—sewage sludge + corn stalk biochar at 450 °C; and 700 °C.</p>
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<p>The heavy metals concentration (mean ± standard deviation) in buckwheat (<b>A</b>) and white mustard (<b>B</b>) shoots after biochar incorporation. Note: SS—sewage sludge; SS + RB<sub>450</sub>—sewage sludge + rapeseed biochar at 450 °C; SS + RB<sub>700</sub>—sewage sludge + rapeseed biochar at 700 °C; SS + DB<sub>450</sub>—sewage sludge + digestate biochar at 450 °C; SS + DB<sub>700</sub>—sewage sludge + digestate biochar at 700 °C; SS + CB<sub>450 and 700</sub>—sewage sludge + corn stalk biochar at 450 °C; and 700 °C.</p>
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<p>The heavy metals concentration (mean ± standard deviation) in lysimetric water, growing buckwheat (<b>A</b>) and white mustard (<b>B</b>). Note: SS—sewage sludge; SS + RB<sub>450</sub>—sewage sludge + rapeseed biochar at 450 °C; SS + RB<sub>700</sub>—sewage sludge + rapeseed biochar at 700 °C; SS + DB<sub>450</sub>—sewage sludge + digestate biochar at 450 °C; SS + DB<sub>700</sub>—sewage sludge + digestate biochar at 700 °C; SS + CB<sub>450 and 700</sub>—sewage sludge + corn stalk biochar at 450 °C; and 700 °C.</p>
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21 pages, 3489 KiB  
Article
Separation and Recovery of Copper and Nickel in the Leachate of a Waste IC Lead Frame through Synergistic Solvent Extraction Using a Binary Extractant Containing LIX984N and Cyanex302 Followed by Selective Stripping
by Li-Pang Wang, Jia-Yan Lin, Yan-Jhang Chen, Bu-Ching Tseng, Ching-Hsiang Hsu, Mingyin Kou, Heng Zhou and Paiboon Sreearunothai
Sustainability 2024, 16(1), 77; https://doi.org/10.3390/su16010077 - 21 Dec 2023
Viewed by 1188
Abstract
The IC lead frame is an essential component in semiconductor packaging, primarily composed of a nickel (Ni)–copper (Cu) alloy in which Ni is electroplated onto a Cu substrate. In this study, synergistic solvent extraction using a binary extractant containing LIX984N and Cyanex302, followed [...] Read more.
The IC lead frame is an essential component in semiconductor packaging, primarily composed of a nickel (Ni)–copper (Cu) alloy in which Ni is electroplated onto a Cu substrate. In this study, synergistic solvent extraction using a binary extractant containing LIX984N and Cyanex302, followed by two-stage selective stripping using sulfuric acid (H2SO4) and nitric acid (HNO3) as the stripping agent, was employed to separate and recover Cu and Ni from the leachate of an IC lead frame. The results indicated that under the optimal conditions of synergistic solvent extraction with an extraction pH value of 1, an extractant concentration of 0.015 M LIX984N + 0.0375 M Cyanex302, an extraction aqueous/organic (A/O) ratio of 1:1, and an extraction time of 5 min, the extraction efficiencies for Cu and Ni were 99.8% and 1.17%, respectively. The distribution ratios were DCu 999 and DNi 0.012, resulting in a separation factor of 83,250. In addition, the separation factor was much higher than that of using individual extractant of LIX984N (6208.3) or Cyanex302 (22,185.2). Subsequently, under optimal first-stage stripping conditions, using 0.05 M H2SO4 at a stripping organic/aqueous (O/A) ratio of 1:1, and with a stripping time of 3 min, a stripping efficiency of 99.9% for Ni was achieved. Next, under optimal second-stage stripping conditions, using 5 M HNO3 at a stripping O/A ratio of 2:1, and with a striping time of 3 min, a stripping efficiency of 99.9% for Cu was achieved. Finally, sodium hydroxide (NaOH) was added to the respective stripping solutions to precipitate Ni and Cu ions, followed by calcination treatment for the precipitates to obtain NiO and CuO, respectively. The purity of the former was 99.74% and that of the latter was 99.82%. The results demonstrate that synergistic solvent extraction using a binary extractant containing LIX984N and Cyanex302 can almost entirely extract Cu in the leachate of an IC lead frame at a lower extraction pH and a lower extractant concentration, thus reducing the co-extraction of Ni. In addition, less co-extracted Ni in the organic phase can be selectively stripped using dilute H2SO4, thus reducing the co-stripping of Cu. Hence, the effective separation and recovery of Cu and Ni in IC lead frame leachate can be achieved, which contributes to improving the sustainability of natural resources. Full article
(This article belongs to the Special Issue EARTH 2022-Green Technologies for Waste Treatment and CO2 Reduction)
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<p>Photograph of the IC lead frame used in this study.</p>
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<p>Experimental setup of this study.</p>
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<p>Effects of extraction pH (<b>a</b>), LIX984N concentration (<b>b</b>), extraction A/O ratio (<b>c</b>), and extraction time (<b>d</b>) on Cu and Ni extraction efficiency using a single extractant of LIX984. Experimental conditions: (<b>a</b>) LIX984N concentration 0.05 M, extraction A/O ratio 1:1, extraction time 10 min; (<b>b</b>) extraction pH 2, extraction A/O ratio 1:1, extraction time 10 min; (<b>c</b>) extraction pH 2, LIX984N concentration 0.05 M, extraction time 10 min; (<b>d</b>) extraction pH 2, LIX984N concentration 0.05 M, extraction A/O ratio 1:1.</p>
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<p>Effects of extraction pH (<b>a</b>), Cyanex302 concentration (<b>b</b>), extraction A/O ratio (<b>c</b>), and extraction time (<b>d</b>) on Cu and Ni extraction efficiency using a single extractant of Cyanex302. Experimental conditions: (<b>a</b>) Cyanex302 concentration 0.05 M, extraction A/O ratio 1:1, extraction time 10 min; (<b>b</b>) extraction pH 1, extraction A/O ratio 1:1, extraction time 10 min; (<b>c</b>) extraction pH 1, Cyanex302 concentration 0.05 M, extraction time 10 min; (<b>d</b>) extraction pH 1, Cyanex302 concentration 0.05 M, extraction A/O ratio 1:1.</p>
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<p>Effects of binary extractant concentration (Cyanex302 concentration was fixed at 0.02 M while varying the LIX984N concentration (<b>a</b>), Cyanex302 concentration was fixed at 0.0375 M while varying the LIX984N concentration (<b>b</b>)), extraction A/O ratio (<b>c</b>), and extraction time (<b>d</b>) on Cu and Ni extraction efficiency using a binary extractant containing LIX984N and Cyanex302. Experimental conditions: (<b>a</b>,<b>b</b>) extraction pH 1, extraction A/O ratio 1:1, extraction time 10 min; (<b>c</b>) extraction pH 1, 0.015 M LIX984N + 0.0375 M Cyanex302, extraction time 10 min; (<b>d</b>) extraction pH 1, 0.015 M LIX984N + 0.0375 M Cyanex302, extraction A/O ratio 1:1.</p>
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<p>Effects of H<sub>2</sub>SO<sub>4</sub> concentration (<b>a</b>), stripping O/A ratio (<b>b</b>), and stripping time (<b>c</b>) on the stripping efficiency for Cu and Ni in the first stage of stripping. Experimental conditions: (<b>a</b>) stripping O/A ratio of 1:1, stripping time of 10 min; (<b>b</b>) H<sub>2</sub>SO<sub>4</sub> concentration of 0.05 M, stripping time of 10 min; (<b>c</b>) H<sub>2</sub>SO<sub>4</sub> concentration of 0.05 M, stripping O/A ratio of 1:1.</p>
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<p>Effects of HNO<sub>3</sub> concentration (<b>a</b>), stripping O/A ratio (<b>b</b>), and stripping time (<b>c</b>) on the stripping efficiency for Cu in the second stage of stripping. Experimental conditions: (<b>a</b>) stripping O/A ratio of 1:1, stripping time of 10 min; (<b>b</b>) HNO<sub>3</sub> concentration of 5 M, stripping time of 10 min; (<b>c</b>) HNO<sub>3</sub> concentration of 5 M, stripping O/A ratio of 2:1.</p>
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<p>Mass balance of Cu and Ni in the present synergistic solvent extraction and selective stripping procedure.</p>
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<p>Effect of precipitation pH on the precipitation efficiency for Cu and Ni ions in the stripping solutions.</p>
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<p>XRD analysis results for the metal oxide calcination products (<b>a</b>) CuO and (<b>b</b>) NiO.</p>
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17 pages, 16840 KiB  
Article
Leachate Experiments to Evaluate Weathering of Waste Rock for Backfill Aquifers in Restored Coal Mine Pits, Powder River Basin, USA
by Julianna Martin and Jeff B. Langman
Geosciences 2024, 14(1), 4; https://doi.org/10.3390/geosciences14010004 - 20 Dec 2023
Cited by 1 | Viewed by 1602
Abstract
Restoration of open-pit mines may utilize waste rock for landscape reconstruction, which can include the construction of backfill aquifers. Weathering and contaminant transport may be different in backfill aquifers compared to the surrounding aquifer because of newly available mineral surfaces and transportable nano- [...] Read more.
Restoration of open-pit mines may utilize waste rock for landscape reconstruction, which can include the construction of backfill aquifers. Weathering and contaminant transport may be different in backfill aquifers compared to the surrounding aquifer because of newly available mineral surfaces and transportable nano- to micro-scale particles generated during mining. Waste rock from the Cordero Rojo open-pit coal mine in the Powder River Basin was exposed to benchtop leachate experiments for 20 weeks at temperatures of 5 °C and 20 °C. Collected leachate was analyzed for Eh, pH, specific conductance, alkalinity, and cation and anion concentrations as unfiltered and 0.45-μm and 0.2-μm filtered concentrations. During the experiment, leachate Eh and pH substantially varied during the first 55 days, which corresponds to a period of high specific conductance (>1000 µS/cm) and alkalinity (>200 mg/L). Correspondingly, anion and cation concentrations were the largest during this early weathering stage, and the filter fractions indicated multiple forms of transported elements. After this early weathering stage, column leachate evolved towards a weathering equilibrium of neutral, oxidizing, and low solute conditions indicated by positive Eh values, pH near 7, and specific conductance <500 μS/cm. This evolution was reflected in the decline and stabilization or non-detection of metal(loid) concentrations reflective of a shift to primarily bulk aluminosilicate weathering when coal- and salt-associated elements, such as arsenic, cadmium, and selenium, were not detected or at minimal concentrations. Over the course of the experiment, the solute trend of certain elements indicated particular weathering processes—cadmium and nanoparticle transport, selenium and salt dissolution, and arsenic and pyrite oxidation. The mining of overburden formations and use of the waste rock for backfill aquifers as part of landscape reconstruction will create newly available mineral surfaces and nanoparticles that will weather to produce solute concentrations not typically found in groundwater associated with the original overburden. Full article
(This article belongs to the Topic Groundwater Pollution Control and Groundwater Management)
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<p>Location of the Cordero Rojo Mine near the town of Gillette in the Powder River Basin of Wyoming, USA (basin boundary from the U.S. Geological Survey).</p>
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<p>Overburden and coal seam at the Cordero Rojo Mine, Powder River Basin, Wyoming, USA.</p>
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<p>Removal of overburden and waste rock generation during open-pit coal mining at the Cordero Rojo Mine, Powder River Basin, Wyoming, USA.</p>
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<p>Element composition of the Fort Union and Wasatch waste rock from the Cordero Rojo Mine.</p>
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<p>(<b>a</b>) Eh, (<b>b</b>) specific conductance, (<b>c</b>) pH, and (<b>d</b>) alkalinity for leachate from the warm- and cold-room columns. All trendlines have been smoothed using the moving window average (4-point window) technique except for Eh.</p>
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<p>Unfiltered (total) and filtered concentrations in the warm-room and cold-room leachates for (<b>a</b>) cadmium and (<b>b</b>) selenium during the first 18 days of the experiment and (<b>c</b>) arsenic during the entire length of the experiment. All non-detect values were set to 0.5 μg/L, which is half the reporting limit for each of the analytes.</p>
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<p>Grain size analysis of waste rock from the pre-experiment Fort Union and Wasatch samples and post-experimental waste rock sampled at three locations from the warm-room leach column (low, middle, and high).</p>
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<p>Activation energy (E<sub>a</sub>) of pyrite weathering derived from warm-room leach column arsenic concentrations during the 20-week experiment.</p>
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<p>Potassium (<b>a</b>) and calcium (<b>b</b>) unfiltered (total) and filtered concentrations for the warm-room and cold-room leachates during the 20-week leach column experiment.</p>
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<p>Iron unfiltered (total) and filtered concentrations for warm-room and cold-room leachates during the 20-week leach column experiment. Non-detect values were set to half the reporting limit (50 μg/L).</p>
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17 pages, 3753 KiB  
Article
Experimental Study on the Desalination of Waste Leachate Using the Combined Freezing Method
by Xiaokai Wang, Changsheng Zhao, Beibei Guo, Bowei Zhang, Xuzhen Liu, Yanke Guo and Yanan Dong
Appl. Sci. 2024, 14(1), 36; https://doi.org/10.3390/app14010036 - 20 Dec 2023
Viewed by 841
Abstract
The current high-salinity wastewater treatment technology is complex, costly, and carries the risk of secondary contamination. As a traditional desalination technology, the combined method using frozen technology has broad development prospects in wastewater treatment. This study investigates the desalination effects of waste leachate [...] Read more.
The current high-salinity wastewater treatment technology is complex, costly, and carries the risk of secondary contamination. As a traditional desalination technology, the combined method using frozen technology has broad development prospects in wastewater treatment. This study investigates the desalination effects of waste leachate using three different methods: the frozen–gravity method (FGM), frozen–centrifugal method (FCM), and frozen–blowing methods (FBMs), under various experimental conditions. The results showed that the salt rejection of all three methods could reach more than 75% under the conditions of a freezing time of 12 h, freezing temperature of −15 °C, and ice production rate of 40%; the salt rejection of FGM increased at higher ambient temperatures, but it was not conducive to the removal of organic pollutants; the salt rejection of FCM was sensitive to the centrifugal time and centrifugal speed, with a significant correlation (p < 0.05), the increase in centrifugal time and centrifugal speed can help to improve the salt rejection, and the increase in centrifugal speed in the range of 1000–2000 rpm can accelerate the discharge of concentrated brine more effectively; the frozen–crushed–blowing method (FCBM) in FBM has a salt rejection as high as 93.86% at an ice production rate of 25.80%, which reduces the salinity of the effluent from 4.07% to 0.25%, speeds up the desalination process, and improves the salt rejection compared to the other methods. This study provides a new perspective and reference for the treatment of high-saline wastewater. Full article
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<p>Changes in the water quality parameters at different freezing times.</p>
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<p>Changes in the water quality parameters at different freezing temperatures.</p>
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<p>Changes in the water quality parameters at different salinities of the solution.</p>
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<p>Microstructural observation diagram of brine bubble vesicles and brine channels at different stages of microscopy: (<b>a</b>) 80% ice production stage, (<b>b</b>) 70% ice production stage, (<b>c</b>) 60% ice production stage, and (<b>d</b>) 50% ice production stage.</p>
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<p>The FGM desalination parameters at different ambient temperatures.</p>
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<p>The FCM desalination parameters at different centrifugal times (speed 2000 rpm).</p>
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<p>The FCM desalination parameters under different centrifugal speeds (time 2 min).</p>
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<p>The relationship between salt rejection and centrifugal time, (<b>a</b>) and the relationship between salt rejection and centrifugal speed (<b>b</b>).</p>
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<p>Desalination parameters of the FGBM on waste leachate (gravity action for 100 min).</p>
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<p>Desalination parameters of the FCBM for waste leachate.</p>
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<p>Quality relationship between the ice crystal melt effluent and discharged concentrate.</p>
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<p>Effect of each method on salt rejection at different salt rejections.</p>
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<p>A system for wastewater desalination and resource recovery and reuse.</p>
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6 pages, 605 KiB  
Proceeding Paper
Effects of Vermicompost Application on Plant Growth Stimulation in Technogenic Soils
by Marketa Dreslova
Eng. Proc. 2023, 57(1), 42; https://doi.org/10.3390/engproc2023057042 - 18 Dec 2023
Viewed by 622
Abstract
The aim of this study was to support the use of waste materials formed from a mixture of technogenic soils for growing plants through adding vermicompost leachates. The effect on the growth of underground and above-ground biomass was evaluated on plants of the [...] Read more.
The aim of this study was to support the use of waste materials formed from a mixture of technogenic soils for growing plants through adding vermicompost leachates. The effect on the growth of underground and above-ground biomass was evaluated on plants of the bush variety of tomato (Solanum lycopersicum). Three different types of biodegradable waste (apple pomace, matolin, and horse manure) were used in the experiments, from which individual vermicomposts were subsequently produced. The effect of the addition of vermicompost leachates to the soil was manifested in all the statistically evaluated parameters of the bush tomato plants. It was found that the highest values were achieved for the root weight (+2.91 g; p < 0.01) and for the stem (+1.92 g, p < 0.01). The lowest values were observed in the control plants without application of the vermicompost leachates. Full article
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<p>The growth of <span class="html-italic">Solanum lycopersicum</span> plants in boxes (author’s photo).</p>
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18 pages, 6098 KiB  
Article
Evaluating the Potential of Multi-Walled Carbon Nanotube-Modified Clay as a Landfill Liner Material
by Xibin Liu, Zhengfa Chen and Lin Qi
Materials 2023, 16(24), 7705; https://doi.org/10.3390/ma16247705 - 18 Dec 2023
Cited by 1 | Viewed by 872
Abstract
In this paper, the feasibility of multi-walled carbon nanotube (MWCNT)-modified clay as a landfill liner material is investigated. Experiments were conducted on the modified clay with 0.5%, 1%, and 2% MWCNTs. The effects of the MWCNTs on the compaction characteristics, permeability coefficient, stress–strain [...] Read more.
In this paper, the feasibility of multi-walled carbon nanotube (MWCNT)-modified clay as a landfill liner material is investigated. Experiments were conducted on the modified clay with 0.5%, 1%, and 2% MWCNTs. The effects of the MWCNTs on the compaction characteristics, permeability coefficient, stress–strain curve, peak deviation stress, shear strength parameters (internal friction angle and cohesion), microstructures, and adsorption performance of the clay were analyzed. The results showed that the optimum moisture content (OMC) increased from 16.15% to 18.89%, and the maximum dry density (MDD) decreased from 1.79 g/cm3 to 1.72 g/cm3 with the increase in MWCNTs. The permeability coefficients firstly fell and then gradually rose as the MWCNTs increased; the minimum permeability coefficient was 8.62 × 10−9 cm/s. The MWCNTs can also effectively increase the peak deviation stress of the clay, and at the maximum level, the peak deviation stress was increased by 286%. SEM images were processed using the Pore and Crack Analysis System (PCAS), and the results showed that the appropriate amount of MWCNTs could fill the pores and strengthen the clay structure. The effect of the MWCNT-modified clay on the adsorption performance of common heavy metal ions Cd2+, Mn2+ and Cu2+ in landfill leachate was analyzed by batch adsorption tests. The maximum adsorption capacities (Qmax) of Cu2+, Cd2+ and Mn2+ in the 2% MWCNT-modified clay were, respectively, 41.67 mg/g, 18.69 mg/g, and 4.97 mg/g. Compared with the clay samples without MWCNTs, the adsorption properties of Cu2+, Cd2+, and Mn2+ were increased by 228%, 124%, and 202%, respectively. Overall, the results suggest that MWCNT-modified clays have the potential to be suitable barrier materials for the construction of landfills. Full article
(This article belongs to the Special Issue Advanced Geomaterials and Reinforced Structures)
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<p>Grain size distribution of the tested clay.</p>
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<p>Microstructure image of MWCNTs.</p>
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<p>(<b>a</b>) photos and (<b>b</b>) sketches of the variable-head permeability instrument.</p>
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<p>Instruments used for UU tests.</p>
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<p>Compaction curves (<b>a</b>) and optimum compaction parameters (<b>b</b>) of clay modified with various MWCNT contents.</p>
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<p>Change in permeability coefficient of modified clay with various MWCNT contents.</p>
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<p>Stress–strain curves of clay modified with different MWCNTs contents: (<b>a</b>) 0%, (<b>b</b>) 0.5%, (<b>c</b>) 1%, (<b>d</b>) 2%.</p>
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<p>Peak deviation stresses in clay modified with different MWCNT contents.</p>
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<p>Cohesion and angle of internal friction of modified clays with different contents of MWCNTs.</p>
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<p>SEM image-processing procedure.</p>
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<p>SEM images of samples with different MWCNT contents: (<b>a</b>) 0%, (<b>b</b>) 0.5%, (<b>c</b>) 1%, and (<b>d</b>) 2%.</p>
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<p>PCAS processing SEM image results.</p>
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<p>Freundlich adsorption isotherms of different heavy metal ions (<b>a</b>) Cu<sup>2+</sup>, (<b>b</b>) Cd<sup>2+</sup>, (<b>c</b>) Mn<sup>2+</sup>.</p>
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<p>Langmuir adsorption isotherms of different heavy metal ions (<b>a</b>) Cu<sup>2+</sup>, (<b>b</b>) Cd<sup>2+</sup>, (<b>c</b>) Mn<sup>2+</sup>.</p>
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22 pages, 5990 KiB  
Article
4D Models Generated with UAV Photogrammetry for Landfill Monitoring Thermal Control of Municipal Solid Waste (MSW) Landfills
by Javier Sedano-Cibrián, Julio Manuel de Luis-Ruiz, Rubén Pérez-Álvarez, Raúl Pereda-García and Jonathan Daniel Tapia-Espinoza
Appl. Sci. 2023, 13(24), 13164; https://doi.org/10.3390/app132413164 - 11 Dec 2023
Cited by 1 | Viewed by 1199
Abstract
The management of the increasing volume of municipal solid waste is an essential activity for the health of the environment and of the population. The organic matter of waste deposited in landfills is subject to aerobic decomposition processes, bacterial aerobic decomposition, and chemical [...] Read more.
The management of the increasing volume of municipal solid waste is an essential activity for the health of the environment and of the population. The organic matter of waste deposited in landfills is subject to aerobic decomposition processes, bacterial aerobic decomposition, and chemical reactions that release large amounts of heat, biogas, and leachates at high temperatures. The control of these by-products enables their recovery, utilization, and treatment for energy use, avoiding emissions to the environment. UAVs with low-cost thermal sensors are a tool that enables the representation of temperature distributions for the thermal control of landfills. This study focuses on the development of a methodology for the generation of 3D thermal models through the projection of TIR image information onto a 3D model generated from RGB images and the identification of thermal anomalies by means of photointerpretation and GIS analysis. The novel methodological approach was implemented at the Meruelo landfill for validation. At the facility, a 4D model (X,Y,Z-temperature) and a 13.8 cm/px GSD thermal orthoimage were generated with a thermal accuracy of 1.63 °C, which enabled the identification of at least five areas of high temperatures associated with possible biogas emissions, decomposing organic matter, or underground fires, which were verified by on-site measurements and photointerpretation of the RGB model, in order to take and assess specific corrective measures. Full article
(This article belongs to the Special Issue Technical Advances in UAV Photogrammetry and Remote Sensing)
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<p>Diagram of the proposed workflow for the 4D model generation and identification of landfill thermal anomalies.</p>
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<p>General overview of the Meruelo MSW landfill and distribution of the different facilities: treatment and recovery plant, landfill, and leachate plant.</p>
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<p>Image of the DJI Mavic 3T UAV which was used for the flight over the landfill.</p>
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<p>Double grip UAV flight plan designed for the Meruelo MSW landfill.</p>
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<p>RGB orthoimage of the MSW landfill.</p>
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<p>3D thermal model (X,Y,Z-temperature) of the MSW landfill. The 4D point cloud provides the position in space and the temperature for each point.</p>
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<p>Thermal orthoimage of the Meruelo MSW landfill.</p>
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<p>Hot spots identified through photointerpretation of the surface temperature distribution in the thermal orthoimage of the Meruelo MSW landfill.</p>
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<p>Detail of the thermal and RGB photointerpretation for the hot spots A and D. These thermal anomalies are due to the exposure of geotextiles in the Meruelo MSW landfill.</p>
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<p>Detail of the thermal and RGB photointerpretation of the hot spot G, which is associated with the leachate collection system.</p>
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<p>Detail of the thermal and RGB photointerpretation of homogeneous terrain areas where the non-justified hot spots B and C are identified.</p>
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<p>Detail of the thermal and RGB photointerpretation of the non-justified hot spot due to stockpiling E.</p>
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<p>Detail of the thermal and RGB photointerpretation of non-justified hot spot F in the oldest area of the landfill.</p>
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<p>The overlapping of the identified hotspots and the LFG recovery well locations enables evaluation of the performance of the emissions control system.</p>
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15 pages, 4808 KiB  
Article
Leachate Tables as a Tool for Monitoring Changes in Physical and Chemical Parameters of the Peat Substrate in the Cells of Nursery Containers
by Michał Jasik, Mariusz Kormanek, Karolina Staszel-Szlachta and Stanisław Małek
Forests 2023, 14(12), 2398; https://doi.org/10.3390/f14122398 - 8 Dec 2023
Viewed by 911
Abstract
Measuring the physical and chemical parameters of substrates in the cells of nursery containers during production is difficult. Monitoring these parameters, however, is required for optimizing the use of substrates and their components in nursery production, specifically important in the progressive reduction in [...] Read more.
Measuring the physical and chemical parameters of substrates in the cells of nursery containers during production is difficult. Monitoring these parameters, however, is required for optimizing the use of substrates and their components in nursery production, specifically important in the progressive reduction in the use of peat. A new solution—leachate tables—for those studies is presented. The leachate tables enable the collection of liquid samples draining from individual cells in nursery containers during long-term irrigation and fertilization. During our 2-month-long experiment, changes in the physical and chemical parameters of the substrate were analyzed, as well as the process of accumulation of elements fed to the substrate via fertilizer and irrigation water. It was found that, due to the different cell volumes, filling the containers with the substrate under the same parameters of vibration and initial moisture resulted in different fractions of the substrate ending up inside the cells. In the smaller cells, the larger diameter fraction was dominant, and in the larger cells, the smaller fraction was dominant. This may have influenced the differences in air and water capacity of the substrate in cells of different volumes and confirmed the need for the selection of individual vibration parameters for the containers. In addition, over time, the granulometric composition of the substrate in the containers changed. Along with the systematic administration of elements via fertilization from the sprinkler ramp, their leachate content increased as a result of increased leaching from the substrate. With time, the physical parameters of the substrate in the cells stabilized, which may have affected the accumulation and leaching of elements during irrigation and fertilization. Full article
(This article belongs to the Special Issue Forest Machinery and Mechanization)
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<p>V150 (<b>left</b>) and V300 (<b>right</b>) containers filled with substrate. Photo: M. Kormanek.</p>
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<p>The scheme of a newly developed station for collecting liquid leachate from container cells with a ramp for irrigation and fertilization–Patent 242506 (specified in <a href="#sec6-forests-14-02398" class="html-sec">Section 6</a>): frame (1), containers (2), sprinkler arm (3), drainage gutters I (4), collecting tank I (5), drawers (6), guides (7), valves (8), collecting tanks II (9), drainage racks (10), measuring cylinders (11), rods with nuts (12), base (13), lower templates (14), upper templates (15), drainage gutters II (16), collecting tank II (17), steel cables (18), protective foil (19).</p>
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<p>Laboratory of irrigation and fertilization techniques for container nurseries with mounted leachate tables.</p>
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<p>Change in the granulometric composition of the substrate over time in the V150 (<b>left</b> figure) and V300 (<b>right</b> figure) containers; T0–T3—terms of collecting samples.</p>
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<p>Change over time of the average statistical diameter of the substrate particles; T0–T3—terms of collecting samples.</p>
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<p>The relationship between elemental content of leachate and physical properties; Dp-average particle diameter; SDP-solid phase density; OP-overall porosity; BD-bulk density; and WC-water capacity, Significance effect * ≤ 0.05.</p>
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