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Search Results (1,205)

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Keywords = atmospheric CO2 concentration

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19 pages, 22817 KiB  
Article
Urban Single Precipitation Events: A Key for Characterizing Sources of Air Contaminants and the Dynamics of Atmospheric Chemistry Exchanges
by Maciej Górka, Aldona Pilarz, Magdalena Modelska, Anetta Drzeniecka-Osiadacz, Anna Potysz and David Widory
Water 2024, 16(24), 3701; https://doi.org/10.3390/w16243701 (registering DOI) - 22 Dec 2024
Viewed by 100
Abstract
The chemistry of atmospheric precipitation serves as an important proxy for discriminating the source(s) of air contaminants in urban environments as well as to discuss the dynamic of atmospheric chemistry exchanges. This approach can be undertaken at time scales varying from single events [...] Read more.
The chemistry of atmospheric precipitation serves as an important proxy for discriminating the source(s) of air contaminants in urban environments as well as to discuss the dynamic of atmospheric chemistry exchanges. This approach can be undertaken at time scales varying from single events to seasonal and yearly time frames. Here, we characterized the chemical composition of two single rain episodes (18 July 2018 and 21 February 2019) collected in Wrocław (SW Poland). Our results demonstrated inner variations and seasonality (within the rain event as well as between summer and winter), both in ion concentrations as well as in their potential relations with local air contaminants and scavenging processes. Coupling statistical analysis of chemical parameters with meteorological/synoptic conditions and HYSPLIT back trajectories allowed us to identify three main factors (i.e., principal components; PC) controlling the chemical composition of precipitation, and that these fluctuated during each event: (i) PC1 (40%) was interpreted as reflecting the long-range transport and/or anthropogenic influences of emission sources that included biomass burning, fossil fuel combustion, industrial processes, and inputs of crustal origin; (ii) PC2 (20%) represents the dissolution of atmospheric CO2 and HF into ionic forms; and (iii) PC3 (20%) originates from agricultural activities and/or biomass burning. Time variations during the rain events showed that each factor was more important at the start of the event. The study of both SO42− and Ca2+ concentrations showed that while sea spray inputs fluctuated during both rain events, their overall impact was relatively low. Finally, below-cloud particle scavenging processes were only observed for PM10 at the start of the winter rain episode, which was probably explained by the corresponding low rain intensity and an overlap from local aerosol emissions. Our study demonstrates the importance of multi-time scale approaches to explain the chemical variability in rainwater and both its relation to emission sources and the atmosphere operating processes. Full article
(This article belongs to the Section Urban Water Management)
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<p>Study sites in Wrocław (SW Poland): University of Wrocław (UWr), where precipitation was collected; IMWM and CIEP air quality monitoring stations.</p>
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<p>Time variations in the meteorological parameters and chemical composition for precipitation samples collected on 18 July 2018: (<b>A</b>) precipitation at IMWM station, wind velocity and air temperature at UWr station, wind rose (24 h); (<b>B</b>) SO<sub>2</sub>, NO<sub>x</sub>, PM<sub>10</sub>, PM<sub>2.5</sub>, O<sub>3</sub> concentrations at CIEP station; (<b>C</b>) anion concentrations in precipitation; (<b>D</b>) pH, EC, and cation concentrations in precipitation.</p>
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<p>Time variations in the meteorological parameters and chemical composition for precipitation samples collected during on 21 February 2019: (<b>A</b>) precipitation at IMWM and UWr stations, wind velocity and air temperature at UWr station, wind rose (24 h); (<b>B</b>) SO<sub>2</sub>, NO<sub>x</sub>, PM<sub>10</sub>, PM<sub>2.5</sub>, O<sub>3</sub> concentrations at CIEP station; (<b>C</b>) anion concentrations in precipitation; (<b>D</b>) pH, EC, and cation concentrations in precipitation.</p>
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<p>The 48 h NOAA HYSPLIT back trajectories showing air mass movement to Wrocław for the (<b>A</b>) summer (18 July 2018) and (<b>C</b>) winter (21 February 2019) precipitation episodes at 12:00 UTC. KNMI synoptic charts (<a href="https://www.knmi.nl" target="_blank">https://www.knmi.nl</a>, accessed on 29 March 2023) corresponding to the two SOM-based weather patterns at 12:00 UTC on (<b>B</b>) 18 July 2018 and (<b>D</b>) 21 February 2021. Prominent synoptic features: L—low-pressure system; H—high-pressure system; blue—cold front; red—warm front; magenta—occluded front.</p>
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<p>Time variations in the calculated concentrations of nSS and SS sulfates and nSS and SS calcium ions in rainwater for the (<b>A</b>,<b>B</b>) summer (18 July 2018) and (<b>C</b>,<b>D</b>) winter (21 February 2019) rain episodes. Equations used for calculations are detailed in the text.</p>
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<p>Time variations in the rainwater sample scores on each principal component analysis (PCA) principal component for (<b>A</b>) summer (18 July 2018) and (<b>B</b>) winter (21 February 2019) precipitation episodes. Results of the PCA for each precipitation event are also presented. Highlighted red values identify significant loadings.</p>
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15 pages, 2495 KiB  
Article
Study of Microalgae Biofixation with Bacteria Carbonic Anhydrase for Carbon Capture and Utilization
by Shui-Shing Chan, Kwan-Shing Chan, Shu-Kei Leung, Wai-Yu Vivian Lam, Ho-Pan Kwok, Tze-Yee Jasmine Yau, Sum-Yi Sammie Wong and Cho-Yin Chan
Sustainability 2024, 16(24), 11196; https://doi.org/10.3390/su162411196 - 20 Dec 2024
Viewed by 342
Abstract
Climate change has been significantly affecting human activities due to the accumulation of greenhouse gases, such as carbon dioxide. Biofixation of carbon dioxide (CO2) has been investigated to reduce the atmospheric CO2 level and slow the rapid increase in the [...] Read more.
Climate change has been significantly affecting human activities due to the accumulation of greenhouse gases, such as carbon dioxide. Biofixation of carbon dioxide (CO2) has been investigated to reduce the atmospheric CO2 level and slow the rapid increase in the global temperature. Carbon capture and utilization (CCU) can be performed by either physio-chemical or biological methods. The latter takes place in ambient temperature and mild conditions, such that there is no need for high pressure and high energy consumption nor hazardous chemicals. Biofixation by microalgae has been utilized to capture CO2 and the microalgae biomass collected after the process can be further utilized in renewable biofuel generation. On the other hand, microbial enzymes, such as carbonic anhydrase (CA), have been investigated to speed up the whole biofixation process by increasing the conversion rate of CO2 into bicarbonate (HCO3) in a culture medium and the latter can be readily used by microalgae to increase CO2 removal. In this study, in the presence of 20% CO2 (v/v) gas in air and 5 mL CA enzyme extract (0.5 mg mL−1 protein), we can significantly increase the biofixation rate using marine green microalgae, Tetraselmis sp. Results showed that the biofixation rate can be increased from 0.64 g L−1 day−1 (no CA and at 0.04% CO2) to 4.26 g L−1 day−1. The effects of different experimental conditions such as pH, nutrient levels and working CO2 concentration levels on Tetraselmis sp. growth and CO2 biofixation (CO2 removal) rate have been investigated. This study demonstrates a new alternative approach for effective carbon capture and utilization (CCU) using microalgae which can be applied to achieve the goal of carbon neutrality. Full article
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<p>Effects of macronutrient N and P levels towards <span class="html-italic">Tetraselmis</span> sp. Growth.</p>
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<p>Effect of different CO<sub>2</sub> levels (%, <span class="html-italic">v</span>/<span class="html-italic">v</span>) towards the pH changes in the culture medium.</p>
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<p>Effects of CO<sub>2</sub> levels towards <span class="html-italic">Tetraselmis</span> sp. growth after 7 days of cultivation (increase in OD<sub>600nm</sub> and final medium pH).</p>
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<p>Kinetic study of CA esterase activity (<b>left:</b> control, no CA, substrate autodecomposition; <b>right:</b> with CA, esterification reaction).</p>
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<p>Effects of CA and CO<sub>2</sub> levels on the growth of <span class="html-italic">Tetraselmis</span> sp.</p>
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<p>Effects of CA and CO<sub>2</sub> levels on medium pH change during the growth of <span class="html-italic">Tetraselmis</span> sp.</p>
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<p>The biofixation rate at different cultivation intervals with different levels of CO<sub>2</sub> and CA.</p>
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<p>Sample cultures of microalgae from Day 0 to Day 7 with different levels of CO<sub>2</sub> and CA.</p>
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<p>Detection of inorganic carbon content and OD<sub>600nm</sub> at specific intervals with different levels of CO<sub>2</sub> and CA.</p>
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24 pages, 18784 KiB  
Article
Large Offsets in the Impacts Between Enhanced Atmospheric and Soil Water Constraints and CO2 Fertilization on Dryland Ecosystems
by Feng Tian, Lei Wang, Ye Yuan and Jin Chen
Remote Sens. 2024, 16(24), 4733; https://doi.org/10.3390/rs16244733 - 18 Dec 2024
Viewed by 332
Abstract
Greening dryland ecosystems greatly benefits from significant CO2 fertilization. This greening trend across global drylands, however, has also been severely constrained by enhancing atmospheric and soil water (SW) deficits. Thus far, the relative offsets in the contributions between the atmospheric vapor pressure [...] Read more.
Greening dryland ecosystems greatly benefits from significant CO2 fertilization. This greening trend across global drylands, however, has also been severely constrained by enhancing atmospheric and soil water (SW) deficits. Thus far, the relative offsets in the contributions between the atmospheric vapor pressure deficit (VPD), SW at varying depths, and CO2 fertilization to vegetation dynamics, as well as the differences in the impacts of decreasing SW at different soil depths on dryland ecosystems over long periods, remain poorly recorded. Here, this study comprehensively explored the relative offsets in the contributions to vegetation dynamics between high VPD, low SW, and rising CO2 concentration across global drylands during 1982–2018 using process-based models and satellite-observed Leaf Area Index (LAI), Gross Primary Productivity (GPP), and solar-induced chlorophyll fluorescence (SIF). Results revealed that decreasing-SW-induced reductions of LAI in dryland ecosystems were larger than those caused by rising VPD. Furthermore, dryland vegetation was more severely constrained by decreasing SW on the subsurface (7–28 cm) among various soil layers. Notable offsets were found in the contributions between enhanced water constraints and CO2 fertilization, with the former offsetting approximately 38.49% of the beneficial effects of the latter on vegetation changes in global drylands. Process-based models supported the satellite-observed finding that increasing water constraints failed to overwhelmingly offset significant CO2 fertilization on dryland ecosystems. This work emphasizes the differences in the impact of SW at different soil depths on vegetation dynamics across global drylands as well as highlights the far-reaching importance of significant CO2 fertilization to greening dryland ecosystems despite increasing atmospheric and SW constraints. Full article
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<p>Temporal dynamics of different satellite-observed vegetation indexes from different datasets in global drylands from 1982 to 2018. (<b>a</b>) LAI, (<b>b</b>) GPP, (<b>c</b>) SIF, and (<b>d</b>) FLUXNET GPP.</p>
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<p>Future trend in long-term series of LAI and GPP in global drylands from 2019 to 2100 derived by 22 ESMs from the CMIP6 projects across different SSP scenarios. (<b>a</b>) LAI, (<b>b</b>) GPP.</p>
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<p>Spatial distribution of interannual trend for vegetation greenness and productivity from different satellite-observed indexes during the period of 1982–2018 is separately presented in (<b>a</b>) averaged LAI trend from three LAI datasets, (<b>b</b>) latitude difference in LAI trend, (<b>c</b>) averaged GPP trend from three GPP datasets, (<b>d</b>) latitude difference in GPP trend, (<b>e</b>) GOSAT SIF trend from 2000 to 2018, and (<b>f</b>) latitude difference of SIF trend. Regions labelled by black dots indicate trends that are statistically significant (MK test; <span class="html-italic">p</span> &lt; 0.05).</p>
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<p>Spatial patterns in the sensitivities of LAI to (<b>a</b>) rising CO<sub>2</sub> concentration, (<b>c</b>) decreasing SW, and (<b>e</b>) increasing atmospheric VPD in global drylands since the early 1980s. Their latitude differences in the sensitivities are shown in (<b>b</b>), (<b>d</b>), and (<b>f</b>), respectively. Regions labelled by black dots represent those trends that are statistically significant at a 95% significance interval (MK test, <span class="html-italic">p</span> &lt; 0.05).</p>
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<p>Spatial patterns in the sensitivities of LAI to SW at the soil depths of (<b>a</b>) 0–7 cm, (<b>b</b>) 7–28 cm, (<b>c</b>) 28–100 cm, and (<b>d</b>) 100–289 cm in global drylands since the early 1980s.</p>
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<p>Spatial patterns of the contributions in LAI changes caused by (<b>a</b>) rising CO<sub>2</sub> concentration, (<b>c</b>) decreasing SW, and (<b>e</b>) increasing atmospheric VPD. Their latitude differences in the contributions are shown in (<b>b</b>), (<b>d</b>), and (<b>f</b>), respectively.</p>
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<p>Differences in LAI changes caused by SW at (<b>a</b>) 0–7 cm soil depth, (<b>b</b>) 7–28 cm soil depth, (<b>c</b>) 28–100 cm soil depth, and (<b>d</b>) 100–289 cm soil depth.</p>
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<p>Comparisons of contributions in the VPD- and SW-induced LAI decreases with CO<sub>2</sub>-induced LAI increases across global drylands from 1982 to 2018. (<b>a</b>) Rising VPD-induced negative contributions counteracting the CO<sub>2</sub>-induced positive contributions, (<b>b</b>) decreasing SW-induced negative contributions counteracting the CO<sub>2</sub>-induced positive contributions, and (<b>c</b>) VPD- and SW-induced negative contributions counteracting the CO<sub>2</sub>-induced positive contributions.</p>
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<p>Statistical distribution of the proportion of the offsetting contributions in different landcovers in global drylands from 1982 to 2018. (<b>a</b>) VPD-induced decreases in LAI offsetting the positive contributions of CO<sub>2</sub> fertilization, defining VPD vs. CO<sub>2</sub>; (<b>b</b>) SW-induced decreases in LAI offsetting the positive contributions of CO<sub>2</sub> fertilization, defining VPD vs. SW; and (<b>c</b>) VPD- and SW-induced decreases in LAI offsetting the positive contributions of CO<sub>2</sub> fertilization, defining VPD+SW vs. CO<sub>2</sub>.</p>
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<p>The differences in the contribution of SW-induced LAI decrease offsetting the CO<sub>2</sub>-induced LAI increases at different soil depths across global drylands from 1982 to 2018: (<b>a</b>) 0–7 cm, (<b>b</b>) 7–28 cm, (<b>c</b>) 28–100 cm, and (<b>d</b>) 100–289 cm.</p>
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<p>Comparison of the contributions of influencing factors on the trend in LAI in global drylands from 1982 to 2018. (<b>a</b>) Multi-model averaging (MMA) of 11 ecosystem models from the TRENDY project and (<b>b</b>) satellite observations.</p>
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26 pages, 13005 KiB  
Article
Analysis of Time–Frequency Characteristics and Influencing Factors of Air Quality Based on Functional Data in Fujian
by Huirou Shen, Yanglan Xiao, Linyi You, Yijing Zheng, Houzhan Xie, Yihan Xu, Zhongzhu Chen, Aidi Wu, Yuning Huang and Tiange You
Atmosphere 2024, 15(12), 1510; https://doi.org/10.3390/atmos15121510 - 17 Dec 2024
Viewed by 289
Abstract
Increased air pollution is driven by anthropogenic pollution emissions and climate change, which pose great challenges to environmental governance. Strengthening the monitoring of regional air quality levels and analyzing the causes of regional pollution is conducive to the management and sustainable development of [...] Read more.
Increased air pollution is driven by anthropogenic pollution emissions and climate change, which pose great challenges to environmental governance. Strengthening the monitoring of regional air quality levels and analyzing the causes of regional pollution is conducive to the management and sustainable development of the regional atmosphere. Functional data obtained on a wavelet basis were used in the fitting of air quality data of Fujian Province, and wavelet decomposition was performed to obtain low-frequency and high-frequency information. While the Fourier basis cannot adaptively adjust the time–frequency window, resulting in the loss of location information of special frequencies, the wavelet basis solves this problem. Functional analysis of variance was utilized for analyzing spatial differences in air pollution characteristics. Furthermore, the study established a multivariate functional linear regression model to explore the impact of meteorological factors and ozone precursor factors. The results indicated that the overall air quality was gradually improving in Fujian Province, but the concentration of ozone was progressively increasing. Air pollution in coastal areas was higher than that in inland areas. The p-values of the functional analysis of variance for energy values and crest values were less than 0.05. Moreover, the energy entropy and kurtosis values were greater than 0.05. There were significant differences of AQI in the fluctuation amplitude and variation characteristics of different cities. The total squared multiple correlation of regression model was above 50% on average. Ozone is currently the most serious pollution factor, mainly affected by wind speed, temperature, NO2, and CO. In summer, it was principally influenced by VOCs. The findings of this study could act as a reference in exploring the time–frequency characteristics of air quality data and support of air pollution control. Full article
(This article belongs to the Section Air Quality)
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<p>Location of the study area (FZ: Fuzhou, LY: Longyan, ND: Ningde, NP: Nanping, PT: Putian, QZ: Quanzhou, SM: Sanming, XM: Xiamen, ZZ: Zhangzhou).</p>
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<p>Flowchart of research methods in the study.</p>
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<p>Overall trend chart of AQI and six pollutants when the decomposition level is 11 (unit: μg/m<sup>3</sup>, except for CO: mg/m<sup>3</sup>).</p>
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<p>LDF and MSE values at different decomposition levels of AQI.</p>
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<p>The AQI and six types of air pollutant curves fitted (unit: μg/m<sup>3</sup>, except for CO: mg/m<sup>3</sup>).</p>
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<p>AQI wavelet variance and cumulative contribution rate.</p>
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<p>Detail components of AQI.</p>
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<p>Detail components of SO<sub>2</sub> (unit: μg/m<sup>3</sup>).</p>
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<p>Detail components of PM<sub>10</sub> (unit: μg/m<sup>3</sup>).</p>
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<p>Detail components of PM<sub>2.5</sub> (unit: μg/m<sup>3</sup>).</p>
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<p>Detail components of O<sub>3</sub> (unit: μg/m<sup>3</sup>).</p>
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<p>Detail components of NO<sub>2</sub> (unit: μg/m<sup>3</sup>).</p>
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<p>Detail components of CO (unit: mg/m<sup>3</sup>).</p>
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<p>AQI energy value box diagram (Group1: FZ, Group 2: LY, Group 3: ND, Group 4: NP, Group 5: PT, Group 6: QZ, Group 7: SM, Group 8: XM, Group 9: ZZ).</p>
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<p>AQI energy entropy box diagram (Group1: FZ, Group 2: LY, Group 3: ND, Group 4: NP, Group 5: PT, Group 6: QZ, Group 7: SM, Group 8: XM, Group 9: ZZ).</p>
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<p>AQI kurtosis box diagram (Group1: FZ, Group 2: LY, Group 3: ND, Group 4: NP, Group 5: PT, Group 6: QZ, Group 7: SM, Group 8: XM, Group 9: ZZ).</p>
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<p>AQI crest value box diagram (Group1: FZ, Group 2: LY, Group 3: ND, Group 4: NP, Group 5: PT, Group 6: QZ, Group 7: SM, Group 8: XM, Group 9: ZZ).</p>
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<p>The left figure shows the total squared multiple correlation, and the right figure shows the squared multiple correlation of ozone precursors CO and NO<sub>2</sub> with O<sub>3</sub> concentration.</p>
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<p>Dynamic changes in the degree of influence of NO<sub>2</sub> concentration, CO concentration, maximum temperature, wind speed, relative humidity, and visibility on O<sub>3</sub> based on the multivariate functional linear model.</p>
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17 pages, 4525 KiB  
Article
Highly Sensitive and Selective SnO2-Gr Sensor Photoactivated for Detection of Low NO2 Concentrations at Room Temperature
by Isabel Sayago, Carlos Sánchez-Vicente and José Pedro Santos
Nanomaterials 2024, 14(24), 1994; https://doi.org/10.3390/nano14241994 - 12 Dec 2024
Viewed by 408
Abstract
Chemical nanosensors based on nanoparticles of tin dioxide and graphene-decorated tin dioxide were developed and characterized to detect low NO2 concentrations. Sensitive layers were prepared by the drop casting method. SEM/EDX analyses have been used to investigate the surface morphology and the [...] Read more.
Chemical nanosensors based on nanoparticles of tin dioxide and graphene-decorated tin dioxide were developed and characterized to detect low NO2 concentrations. Sensitive layers were prepared by the drop casting method. SEM/EDX analyses have been used to investigate the surface morphology and the elemental composition of the sensors. Photoactivation of the sensors allowed for detecting ultra-low NO2 concentrations (100 ppb) at room temperature. The sensors showed very good sensitivity and selectivity to NO2 with low cross-responses to the other pollutant gases tested (CO and CH4). The effect of humidity and the presence of graphene on sensor response were studied. Comparative studies revealed that graphene incorporation improved sensor performance. Detections in complex atmosphere (CO + NO2 or CH4 + NO2, in humid air) confirmed the high selectivity of the graphene sensor in near-real conditions. Thus, the responses were of 600%, 657% and 540% to NO2 (0.5 ppm), NO2 (0.5 ppm) + CO (5 ppm) and NO2 (0.5 ppm) + CH4 (10 ppm), respectively. In addition, the detection mechanisms were discussed and the possible redox equations that can change the sensor conductance were also considered. Full article
(This article belongs to the Special Issue Advanced Nanomaterials in Gas and Humidity Sensors)
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Graphical abstract
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<p>(<b>a</b>) SEM micrographs and (<b>b</b>) EDX elemental mapping images of one sensitive layer (SnO<sub>2</sub>-Gr).</p>
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<p>TEM images of (<b>a</b>) Gr-SnO<sub>2</sub> on grids (<b>b</b>) pristine SnO<sub>2</sub> nanoparticles, (<b>c</b>) Gr-SnO<sub>2</sub> and (<b>d</b>) HRTEM images of Gr-SnO<sub>2</sub>.</p>
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<p>Resistance changes in the SnO<sub>2</sub>-NPs sensor tested with and without UV-LED illumination at RT in air.</p>
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<p>SnO<sub>2</sub> sensor: (<b>a</b>) Dynamic response to NO<sub>2</sub> at RT in air atmosphere with and without UV-LED illumination and (<b>b</b>) responses to 0.5 ppm NO<sub>2</sub> under different conditions (with and without UV-LED, dry and humid air).</p>
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<p>Dynamic response curves at RT under UV-LED illumination to NO<sub>2</sub> different concentrations of the tested sensors: (<b>a</b>) SnO<sub>2</sub> and (<b>b</b>) SnO<sub>2</sub>-Gr. (<b>c</b>) Response of the SnO<sub>2</sub> and SnO<sub>2</sub>-Gr sensors to 0.1, 0.3 and 0.5 ppm NO<sub>2</sub> at RT under UV-LED illumination in dry and humid air (50% RH). (<b>d</b>) Sensor responses versus NO<sub>2</sub> gas concentration in dry and humid air (50% RH) with UV-LED illumination, where the circles denote experimental results and the dotted lines represent fitting curves.</p>
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<p>(<b>a</b>) Responses of the sensors to 0.3 ppm NO<sub>2</sub>, 5 ppm CO and 5 ppm CH<sub>4</sub> in dry and wet air. (<b>b</b>) Selectivity of the tested sensors to NO<sub>2</sub> at RT and under UV-LED illumination, in dry and humid air (50%). SnO<sub>2</sub>-Gr sensor dynamic response at RT in humid air (45% RH) and under UV-LED illumination to different gas mixtures: (<b>c</b>) mixture 1 (NO<sub>2</sub> + CO) (<b>d</b>) mixture 2 (NO<sub>2</sub> + CH<sub>4</sub>).</p>
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<p>Detection mechanism scheme.</p>
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12 pages, 701 KiB  
Article
Functional Near-Infrared Spectroscopy Analysis of Cerebral Physiological Changes in Response to Atmospheric Gas Concentrations
by Chan-Sol Park, Mu-Jin Kim, Dong-Hyun Kim, Yeong-Bae Lee and Chang-Ki Kang
Appl. Sci. 2024, 14(24), 11525; https://doi.org/10.3390/app142411525 - 11 Dec 2024
Viewed by 369
Abstract
Compared with other organs in the body, the human brain is extremely sensitive to changes in O2 and CO2 levels. This study applied functional near-infrared spectroscopy (fNIRS) to analyze the changes in cerebral oxygen saturation (COS) and hemoglobin (Hb) concentrations in [...] Read more.
Compared with other organs in the body, the human brain is extremely sensitive to changes in O2 and CO2 levels. This study applied functional near-infrared spectroscopy (fNIRS) to analyze the changes in cerebral oxygen saturation (COS) and hemoglobin (Hb) concentrations in response to various atmospheric gas concentrations and investigate their effects on brain function. Twenty-nine adults were exposed to four gas conditions, namely atmospheric concentration (C1), high O2 concentration (C2), high CO2 concentration (C3), and high O2 and CO2 concentrations (C4). Changes in COS and Hb concentrations were measured using fNIRS, whereas heart rate (HR) and percutaneous oxygen saturation (SpO2) were measured using a patient monitor. COS, oxy-Hb (HbO), and total-Hb (HbT) increased progressively from C1 to C4, whereas deoxy-Hb (HbR) exhibited a decreasing trend. Moreover, the COS and Hb concentrations were more strongly influenced by high CO2 levels than by high O2 levels. High O2 concentrations increased the blood O2 saturation, whereas high CO2 concentrations increased blood flow as a physiological response, enhancing O2 delivery to the brain. Additionally, HR and SpO2 increased at high CO2 concentrations. However, at high O2 concentrations providing a sufficient O2 supply, SpO2 increased while HR decreased. Therefore, adjusting the concentrations of CO2 and O2 may improve cerebral blood flow and change brain function, supporting cerebrovascular health and preventing related diseases. Full article
(This article belongs to the Special Issue Air Pollution and Its Impact on the Atmospheric Environment)
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<p>Workflow for the comparison of the vertical and radial projection methods.</p>
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<p>Workflow for the comparison of the vertical and radial projection methods.</p>
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18 pages, 6803 KiB  
Article
Vegetation and Precipitation Patterns Define Annual Dynamics of CO2 Efflux from Soil and Its Components
by Dmitriy Khoroshaev, Irina Kurganova, Valentin Lopes de Gerenyu, Dmitry Sapronov, Sergey Kivalov, Abeer S. Aloufi and Yakov Kuzyakov
Land 2024, 13(12), 2152; https://doi.org/10.3390/land13122152 - 11 Dec 2024
Viewed by 434
Abstract
Respiration of soil heterotrophs—mainly of bacteria and fungi—is a substantial part of carbon balance in terrestrial ecosystems, which tie up organic matter decomposition with the rise of atmospheric CO2 concentration. Deep understanding and prediction of seasonal and interannual variation of heterotrophic and [...] Read more.
Respiration of soil heterotrophs—mainly of bacteria and fungi—is a substantial part of carbon balance in terrestrial ecosystems, which tie up organic matter decomposition with the rise of atmospheric CO2 concentration. Deep understanding and prediction of seasonal and interannual variation of heterotrophic and autotrophic components of CO2 efflux from soil is limited by the lack of long-term, full-year measurements. To better understand the impact of current climate changes on CO2 emissions from soils in the mixed forest and mowed grassland, we measured CO2 efflux every week for 2 years. Heterotrophic (SOM-derived + leaf litter) and root-associated (root with rhizosphere microorganisms) components were partitioned by the root exclusion method. The total CO2 efflux from soil was averaged 500 g C m−2 yr−1 in the forest and 650 g C m−2 yr−1 in the grassland, with shares of the no-growing cold season (Nov–Mar) of 22% and 14%, respectively. The heterotrophic component of CO2 efflux from the soil averaged 62% in the forest and 28% in the grassland, and it was generally stable across seasons. The redistribution of the annual precipitation amounts as well as their deficit (droughts) reduced soil respiration by 33–81% and heterotrophic respiration by 24–57% during dry periods. This effect was more pronounced in the grassland (with an average decline of 56% compared to 39% in the forest), which is related to lower soil moisture content in the grassland topsoil during dry periods. Full article
(This article belongs to the Section Land–Climate Interactions)
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<p>General view of the vegetation and soils within the native mixed forest (<b>a</b>) and mowed grassland (<b>b</b>) ecosystems, along with chambers for soil respiration measurements during warm (<b>b</b>) and cold (<b>c</b>) periods. The process of installing soil chambers containing root-free soils (<b>d</b>).</p>
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<p>Dynamics of air (Ta) and soil (Ts) temperatures and height of snow cover (<b>a</b>), soil and forest litter moisture content (<b>b</b>) during the measurements of soil respiration (SR) and respiration of SOM−derived microorganisms (HR) in the forest (<b>c</b>) and the grassland (<b>d</b>). The dotted lines for HR show values reconstructed using the regression method for the first half of June 2022. Arrows indicate the decrease in SR and HR values during prolonged dry periods: August 2022, June 2023, and September 2023. Error bars are standard errors of the mean.</p>
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<p>Dynamics of air (Ta) temperatures, day sum precipitation (P), soil moisture content (Ww) during the measurements of soil respiration (SR) and respiration of SOM-derived microorganisms (HR) in the grassland (<b>a</b>,<b>c</b>) and the forest (<b>b</b>,<b>d</b>) during summer–autumn periods of 2022 (<b>a</b>,<b>b</b>) and 2023 (<b>c</b>,<b>d</b>).</p>
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<p>Soil respiration (SR) and soil moisture content (Ww) relationships during summer–autumn periods of 2022 (<b>a</b>,<b>b</b>) and 2023 (<b>c</b>,<b>d</b>) in the forest and the grassland. Data for the whole June–September period (<b>a</b>,<b>c</b>) and for periods with a high amount of dry days: 26 June–8 August 2022 (<b>b</b>) as well as June and 29 August–4 October 2023 (<b>d</b>).</p>
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<p>Dynamics of total monthly soil (SR), SOM-derived heterotrophs (HR), and root-derived (RR) respiration values (<b>a</b>–<b>c</b>) and their distribution over two years (<b>d</b>–<b>f</b>): the median (bar), lower (Q1) and upper (Q3) quartiles (“boxes”); X1 = Q1 − 1.5 IQR (interquartile range, IQR = Q3 − Q1) and X2 = Q3 − 1.5 IQR (“moustaches”); all data are shown as dots.</p>
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<p>Differences in the total monthly soil (SR), SOM-derived heterotrophs (HR), and root-derived (RR) respiration between the grassland and forest ecosystems (<b>a</b>); a positive value means more intensive fluxes in the grassland. Dynamics of the share of monthly HR in SR values in the ecosystems (<b>b</b>). The relationships between increments of HR or RR and SR (<b>c</b>) values presented in (<b>a</b>), as well as the increments of HR shares between the forest and the grassland (<b>d</b>).</p>
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<p>Offset of SOM-derived respiration of heterotrophs (HR) measured in young (installed in June–July 2023) soil chambers relative to mature (installed in May 2022) soil chambers, in terms of absolute (<b>a</b>) and relative (<b>b</b>) values. A cross mark indicates days with no significant differences (<span class="html-italic">t</span>-test with equal variances, n = 4–5, <span class="html-italic">p</span> &lt; 0.05).</p>
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<p>Offset of soil moisture content (SMC) at the depth of 0–6 cm within soil chambers without roots relative to surrounding intact soil, in terms of absolute (<b>a</b>) and relative (<b>b</b>) values. A cross mark indicates days with no significant differences (<span class="html-italic">t</span>-test with equal variances, n = 5–10, <span class="html-italic">p</span> &lt;0.05).</p>
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<p>Respiration of soil (SR) and its SOM-derived (HR) and root-derived components (RR) during 2022–2023 (<b>a</b>) and during 2023–2024 (<b>b</b>): the mean (cross), the median (bar), lower (Q1), and upper (Q3) quartiles (“boxes”); X1 = Q1 − 1.5 IQR (interquartile range, IQR = Q3 − Q1) and X2 = Q3 − 1.5 IQR (“moustaches”); all data are shown as dots. Different letters indicate pairs of average values, the differences of which are detected during the multiple comparison procedure (Tukey test, α = 5%) after two-way ANOVA (Flux component × Ecosystem).</p>
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<p>The regression functions of SOM-derived microorganisms respiration rate (HR) based on soil respiration rate (SR) was developed using data from 20 July 2022 to 29 September 2022, which was then used to reconstruct HR for the period from 1 July 2022 to 14 July 2022.</p>
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19 pages, 1444 KiB  
Review
Possible Impacts of Elevated CO2 and Temperature on Growth and Development of Grain Legumes
by Rajanna G. Adireddy, Saseendran S. Anapalli, Krishna N. Reddy, Partson Mubvumba and Justin George
Environments 2024, 11(12), 273; https://doi.org/10.3390/environments11120273 - 2 Dec 2024
Viewed by 695
Abstract
Carbon dioxide (CO2) is the most abundant greenhouse gas (GHG) in the atmosphere and the substrate for the photosynthetic fixation of carbohydrates in plants. Increasing GHGs from anthropogenic emissions is warming the Earth’s atmospheric system at an alarming rate and changing [...] Read more.
Carbon dioxide (CO2) is the most abundant greenhouse gas (GHG) in the atmosphere and the substrate for the photosynthetic fixation of carbohydrates in plants. Increasing GHGs from anthropogenic emissions is warming the Earth’s atmospheric system at an alarming rate and changing its climate, which can affect photosynthesis and other biochemical reactions in crop plants favorably or unfavorably, depending on plant species. For the substrate role in plant carbon reduction reactions, CO2 concentration ([CO2]) in air potentially enhances photosynthesis. However, N uptake and availability for protein synthesis can be a potential limiting factor in enhanced biomass synthesis under enriched [CO2] conditions across species. Legumes are C3 plants and symbiotic N fixers and are expected to benefit from enhanced [CO2] in the air. However, the concurrent increase in air temperatures with enhanced [CO2] demands more detailed investigations on the effects of [CO2] enhancement on grain legume growth and yield. In this article, we critically reviewed and presented the online literature on growth, phenology, photosynthetic rate, stomatal conductance, productivity, soil health, and insect behavior under elevated [CO2] and temperature conditions. The review revealed that specific leaf weight, pod weight, and nodule number and weight increased significantly under elevated [CO2] of up to 750 ppm. Under elevated [CO2], two mechanisms that were affected were the photosynthesis rate (increased) and stomatal conductivity (decreased), which helped enhance water use efficiency in the C3 legume plants to achieve higher yields. Exposure of legumes to elevated levels of [CO2] when water stressed resulted in an increase of 58% in [CO2] uptake, 73% in transpiration efficiency, and 41% in rubisco carboxylation and decreased stomatal conductance by 15–30%. The elevated [CO2] enhanced the yields of soybean by 10–101%, peanut by 28–39%, mung bean by 20–28%, chickpea by 26–31%, and pigeon pea by 31–38% over ambient [CO2]. However, seed nutritional qualities like protein, Zn, and Ca were significantly decreased. Increased soil temperatures stimulate microbial activity, spiking organic matter decomposition rates and nutrient release into the soil system. Elevated temperatures impact insect behavior through higher plant feeding rates, posing an enhanced risk of invasive pest attacks in legumes. However, further investigations on the potential interaction effects of elevated [CO2] and temperatures and extreme climate events on growth, seed yields and nutritional qualities, soil health, and insect behavior are required to develop climate-resilient management practices through the development of novel genotypes, irrigation technologies, and fertilizer management for sustainable legume production systems. Full article
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<p>Response of legumes to elevated [CO<sub>2</sub>] and temperature measured from open-top chambers, free-air [CO<sub>2</sub>] enrichment experiments (FACE), and controlled indoor and outdoor growth chambers.</p>
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<p>Response of elevated [CO<sub>2</sub>] and temperature in legume crops. [<a href="#B1-environments-11-00273" class="html-bibr">1</a>,<a href="#B6-environments-11-00273" class="html-bibr">6</a>,<a href="#B98-environments-11-00273" class="html-bibr">98</a>].</p>
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26 pages, 2875 KiB  
Article
Temporal Variations, Air Quality, Heavy Metal Concentrations, and Environmental and Health Impacts of Atmospheric PM2.5 and PM10 in Riyadh City, Saudi Arabia
by Hattan A. Alharbi, Ahmed I. Rushdi, Abdulqader Bazeyad and Khalid F. Al-Mutlaq
Atmosphere 2024, 15(12), 1448; https://doi.org/10.3390/atmos15121448 - 30 Nov 2024
Viewed by 643
Abstract
Atmospheric particulate matter (PM) samples were collected in Riyadh, Saudi Arabia, to assess air quality, quantify, heavy metal concentrations, and evaluate related ecological and health risks. This study’s uniqueness stems from its focused and detailed analysis of PM pollution in Riyadh, including an [...] Read more.
Atmospheric particulate matter (PM) samples were collected in Riyadh, Saudi Arabia, to assess air quality, quantify, heavy metal concentrations, and evaluate related ecological and health risks. This study’s uniqueness stems from its focused and detailed analysis of PM pollution in Riyadh, including an extensive assessment of heavy metal concentrations across different PM sizes by applying diverse pollution and health indices. This brings to light critical health and ecological issues and provides foundation for targeted pollution control efforts in the region. The study focused on two PM size fractions, PM2.5 and PM10 and analyzed the presence of heavy metals, including iron (Fe), nickel (Ni), chromium (Cr), zinc (Zn), cobalt (Co), copper (Cu), silver (Ag), arsenic (As), cadmium (Cd), and lead (Pb), using inductively coupled plasma emission spectrometry. Results showed significantly higher levels of PM10 (223.12 ± 66.12 µg/m3) compared to PM2.5 (35.49 ± 9.63 µg/m3), suggesting that local dust is likely a primary source. Air quality varied from moderate to unhealthy, with PM10 posing substantial risks. Heavy metal concentrations in PM2.5 followed the order Fe (13.14 ± 11.66 ng/m3) > As (2.87 ± 2.08 ng/m3) > Cu (0.71 ± 0.51 ng/m3) > Zn (0.66 ± 0.46 ng/m3) > Cr 0.50 ± 0.23 ng/m3) > Pb (0.14 ± 0.10 ng/m3) > Ni (0.03 ± 0.04 ng/m3) > Cd (0.004 ± 0.002 ng/m3) > Ag (0.003 ± 0.003 ng/m3) > Co (0.002 ± 0.004 ng/m3). In PM10, they followed the order Fe (743.18 ± 593.91 ng/m3) > As (20.12 ± 13.03 ng/m3) > Cu (10.97 ± 4.66 ng/m3) > Zn (9.06 ± 5.50 ng/m3) > Cr (37.5 ± 2.70 ng/m3) > Ni (1.72 ± 01.54 ng/m3) > Pb (1.11 ± 0.64 ng/m3) > Co (0.25 ± 0.28 ng/m3) > Ag (0.10 ± 0.26 ng/m3) > Cd (0.04 ± 0.02 ng/m3). Enrichment factor analysis revealed elevated levels for the metals Cu, Zn, As, Ag, Cd, and Pb. Pollution indices indicated various contamination levels, with Ag and As showing particularly high contamination and ecological risks. The study highlighted significant health concerns, especially from As, which poses a substantial long-term carcinogenic threat. The findings emphasize the urgent need to reduce hazardous metal levels in Riyadh’s air, especially with high child exposure. Full article
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<p>Maps showing the locations of (<b>a</b>) Saudi Arabia, (<b>b</b>) Riyadh city, and (<b>c</b>) the sampling site indicated by the dotted circle and letter S. (The world in Arabic الرياض refers to Riyadh).</p>
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<p>The concentrations in µg/m<sup>3</sup> of (<b>a</b>) PM<sub>2.5</sub> and PM<sub>10</sub>, (<b>b</b>) ratio of PM<sub>10</sub>/PM<sub>2.5</sub>, and (<b>c</b>) the air quality index (AQI, EPA, 1999) of both PM<sub>2.5</sub> and PM<sub>10</sub> in Riyadh city during period of April to December 2023.</p>
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<p>Temporal concentrations of major and heavy metals in atmospheric PM<sub>2.5</sub> and PM<sub>10</sub> samples collected from Riyadh city, Saudi Arabia from April to September of 2023.</p>
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<p>Dendrograms of cluster analyses (CA) for the heavy metals in atmospheric PM<sub>2.5</sub> and PM<sub>10</sub> from the city of Riyadh–Saudi Arabia during the period of April to December 2023. The dendrograms presented in <a href="#atmosphere-15-01448-f004" class="html-fig">Figure 4</a> identified four cluster groups (A, B, C, and D) for PM<sub>2.5</sub>.</p>
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<p>Box plots showing the indices of contamination degree (CD) (if the value &lt;6 = low; 6 &lt; CD &lt; 12 = moderate, 12 &lt; CD &lt; 24 = significant, CD &gt; 24 = high), pollution load index (PLI: PLI ≤ 0 no contamination 0 &lt; PLI &lt; 1 = baseline contamination PLI &gt; 1 = high contamination), Nemerow pollution index (NPI: NPI ≤ 0.7 = Unpolluted, 0.7–1 = warning line pollution, 1–2 = low pollution, 2–3 = moderately polluted, &gt;3 = Strongly polluted), Nemerow risk index (NRI: NRI ≤ 40 = low risk, 40 &lt; NRI ≤ 80 = moderate risk, 80 &lt; NRI ≤ 160 = considerable risk, 160 &lt; NRI ≤ 320 = high risk, NRI &gt; 320 = very high risk), (RI: RI &lt; 150 = low ecological risk, 150 ≤ RI &lt; 300 = moderate ecological risk, 300 ≤ RI &lt; 600 = considerable ecological risk, RI ≥ 600 = very high ecological risk) and toxic risk index (TRI: TRI ≤ 5 = no toxic risk, 5–10 = low toxic risk, 10–15 = moderate toxic risk, 15–20 = considerable toxic risk, &gt;20 = very high toxic risk) for the heavy metals determined in atmospheric PM<sub>2.5</sub> and PM<sub>10</sub> from Riyadh city-Saudi Arabia.</p>
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16 pages, 6035 KiB  
Article
CO2 Emission from Caves by Temperature-Driven Air Circulation—Insights from Samograd Cave, Croatia
by Nenad Buzjak, Franci Gabrovšek, Aurel Perșoiu, Christos Pennos, Dalibor Paar and Neven Bočić
Climate 2024, 12(12), 199; https://doi.org/10.3390/cli12120199 - 26 Nov 2024
Viewed by 1049
Abstract
Opposite to atmospheric CO2 concentrations, which reach a minimum during the vegetation season (e.g., June–August in the Northern Hemisphere), soil CO2 reaches a maximum in the same period due to the root respiration. In karst areas, characterized by high rock porosity, [...] Read more.
Opposite to atmospheric CO2 concentrations, which reach a minimum during the vegetation season (e.g., June–August in the Northern Hemisphere), soil CO2 reaches a maximum in the same period due to the root respiration. In karst areas, characterized by high rock porosity, this excess CO2 seeps inside caves, locally increasing pCO2 values above 1%. To better understand the role of karst areas in the carbon cycle, it is essential to understand the mechanisms of CO2 dynamics in such regions. In this study, we present and discuss the spatial and temporal variability of air temperature and CO2 concentrations in Samograd Cave, Croatia, based on three years of monthly spot measurements. The cave consists of a single descending passage, resulting in a characteristic bimodal climate, with stable conditions during summer (i.e., stagnant air inside the cave) and a strong convective cell bringing in cold air during winter. This bimodality is reflected in both CO2 concentrations and air temperatures. In summer, the exchange of air through the cave’s main entrance is negligible, allowing the temperature and CO2 concentration to equilibrate with the surrounding rocks, resulting in high in-cave CO2 concentrations, sourced from enhanced root respiration. During cold periods, CO2 concentrations are low due to frequent intrusions of fresh external air, which effectively flush out CO2 from the cave. Both parameters show distinct spatial variability, highlighting the role of cave morphology in their dynamics. The CO2 concentrations and temperatures have increased over the observation period, in line with external changes. Our results highlight the role of caves in transferring large amounts of CO2 from soil to the atmosphere via caves, a process that could have a large impact on the global atmospheric CO2 budget, and thus, call for a more in-depth study of these mechanisms. Full article
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<p>Samograd Cave location map and cave map with spot measurement locations (blue). Survey: Neven Bočić and Dinko Stopić, 2011.</p>
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<p>Monthly air temperature (lines; T1t–T12t) and pCO<sub>2</sub> (vertical bars; T1–T12) variability in Samograd Cave (March 2021 to February 2024). The colors of the bars and lines are decreasing with increasing distance from cave entrance (dark colors) to cave interior (light colors).</p>
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<p>Range of air temperature variability (purple) in Samograd Cave.</p>
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<p>Statistics of <span class="html-italic">p</span>CO<sub>2</sub> variability in Samograd Cave at locations T12 to T5 (external locations T1 and T2 excluded), described by maximum (Max), minimum (Min), range, mean, median, and standard deviation (SD) values.</p>
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<p>Statistics of T<sub>air</sub> variability in Samograd Cave at locations T12 to T5 (external locations T1 and T2 excluded), described by maximum (Max), minimum (Min), range, mean, median, and standard deviation (SD) values.</p>
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<p>Correlation coefficients between external (T1) and in-cave air temperatures in Samograd Cave at locations T2–T5.</p>
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<p>The 2021–2024 variability of global <span class="html-italic">p</span>CO<sub>2</sub> vs. average cave <span class="html-italic">p</span>CO<sub>2</sub> in Samograd Cave with trendlines (dashed).</p>
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<p>Seasonal variations in the spatial distribution of T<sub>air</sub> values and CO<sub>2</sub> concentrations in Samograd Cave: A comparison of values between January and August 2023. Measurements were taken along the cave’s longitudinal profile, and the plan-view data were interpolated across the cave’s full width using the Inverse Distance Weighting (IDW) method in ArcGIS Pro 3.2 to demonstrate changes in T<sub>air</sub> values and CO<sub>2</sub> concentrations across both time and space. In the profile view, interpolation was restricted to a 2 m high buffer. The gray gradation, from light at the entrance zone to dark at the cave’s end, symbolically represents the diminishing influence of surface conditions, which substantially affect T<sub>air</sub> and CO<sub>2</sub>.</p>
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<p>Conceptual model of CO<sub>2</sub> dynamics in Samograd Cave (pink color represents CO<sub>2</sub>). In summer (panel (<b>a</b>)), root respiration and soil microbial activity produces CO<sub>2</sub> which fills the spaces inside the limestone, creating a CO<sub>2</sub> reservoir that also fills the cave. In winter (panel (<b>b</b>)), cold air inflow pushes CO<sub>2</sub> out of the cave. The resulting low <span class="html-italic">p</span>CO<sub>2</sub> in the cave increases the transfer of CO<sub>2</sub> from the ground reservoir to the cave’s atmosphere, being further exported via the temperature-driven air circulation.</p>
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18 pages, 4915 KiB  
Article
Application of Pseudomonas cepacia CCT 6659 Biosurfactant as a Metal Corrosion Inhibitor in a Constructed Accelerated Corrosion Chamber (ACC)
by Rita de Cássia F. Soares da Silva, Alexandre Augusto P. Selva Filho, Yslla Emanuelly S. Faccioli, Yasmim K. Silva, Kaio W. Oliveira, Gleice Paula Araujo, Nathália Maria P. Rocha e Silva, Attilio Converti and Leonie A. Sarubbo
Fermentation 2024, 10(12), 602; https://doi.org/10.3390/fermentation10120602 - 25 Nov 2024
Viewed by 678
Abstract
Corrosion is the deterioration of metals due to environmental exposure. Commercial inhibitors used to control corrosion often contain heavy metal salts, which are highly toxic to both the environment and human health. A biosurfactant produced by the bacterium Pseudomonas cepacia CCT 6659 was [...] Read more.
Corrosion is the deterioration of metals due to environmental exposure. Commercial inhibitors used to control corrosion often contain heavy metal salts, which are highly toxic to both the environment and human health. A biosurfactant produced by the bacterium Pseudomonas cepacia CCT 6659 was tested as a corrosion inhibitor on carbon steel and galvanized iron surfaces. Matrices based on plant ingredients with different compositions were tested in a laboratory-constructed accelerated corrosion chamber (ACC) simulating a critical maritime atmosphere in conditions of 40 °C, 5% NaCl, and 100% humidity. The most stable matrix was selected for biosurfactant incorporation in different concentrations, expressed as critical micellar concentration (CMC), and was applied to metal surfaces to evaluate its ability to inhibit corrosion. Additionally, to evaluate the potential of the biosurfactant as a low-toxicity corrosion inhibitor additive in paint systems, iron and carbon steel samples were coated with three biosurfactant-containing commercial paints and subjected to critical atmospheric conditions for testing coating effectiveness. The formulation containing vegetable resin as a plasticizer, oleic acid, ethanol, and CaCO3 was chosen to incorporate the biosurfactant. The addition of the biosurfactant at twice its CMC led to a reduction in carbon steel sample mass loss from 123.6 to 82.2 g/m2, while in the galvanized iron plates, the mass loss decreased from 285.9 to 226.7 g/m2 at the same biosurfactant concentration. When supplemented with the biosurfactant, the alkyd resin-based paint (A) ensured less mass loss in samples (46.0 g/m2) compared to the control without biosurfactant (58.0 g/m2). Using the paint formulated with oil-based resin (B), the mass loss decreased from 53.0 to 24.1 g/m2, while with that based on petroleum derivatives (C), it decreased from 82.2 to 27.6 g/m2. These results confirm the feasibility of using biosurfactants in biodegradable coatings, reducing the need for commercial corrosion inhibitors. Full article
(This article belongs to the Section Industrial Fermentation)
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<p>Stages for obtaining biosurfactant from <span class="html-italic">Pseudomonas cepacia</span> CCT 6659 involving fermentation in a mineral medium enhanced with 2.0% residual frying canola oil and 3.0% corn steep liquor, followed by the recovery of the concentrated biosurfactant extract.</p>
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<p>Flow diagram of physical agents in the accelerated corrosion chamber.</p>
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<p>(<b>A</b>) Entry of salt mist into the accelerated corrosion chamber. (<b>B</b>) Carbon steel test specimens placed in the accelerated corrosion chamber.</p>
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<p>(<b>A</b>) Preparation of the matrix based on vegetable resin. Heating and solubilization of the resin in oleic acid. (<b>B</b>) Dispersion of CaCO<sub>3</sub> in the solvent. (<b>C</b>) Homogenization of the two phases until the formation of a uniform suspension.</p>
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<p>Test specimens coated with (<b>A</b>) the vegetable resin-based matrix and (<b>B</b>) the synthetic coating (corrosion inhibitor primer).</p>
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<p>Details of the accelerated corrosion chamber built in the laboratory.</p>
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<p>Test specimens after 15 days of exposure to salt spray in the accelerated corrosion chamber.</p>
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<p>Mass loss per area after 30 days of critical atmospheric dynamic simulation of carbon steel specimens incorporating matrices based on rosin resin, oleic acid, xylene, and CaCO<sub>3</sub>; rosin resin, oleic acid, acetone, and CaCO<sub>3</sub>; rosin resin, xylene, acetone, and CaCO<sub>3</sub>; rosin resin, oleic acid, ethanol, and CaCO<sub>3</sub> and commercial coating (corrosion inhibitor primer).</p>
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<p>Test specimens after 30 days of exposure to salt spray in the accelerated corrosion chamber. (<b>A</b>) Control: biodegradable matrix without biosurfactant, (<b>B</b>) biodegradable matrix with incorporated biosurfactant, and (<b>C</b>) commercial coating (corrosion inhibitor primer).</p>
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<p>Mass loss per area after 30 days of exposure to salt spray in the accelerated corrosion chamber in galvanized iron and carbon steel plates in biodegradable matrix with or without biosurfactant at different concentrations, namely, 1/2 CMC, CMC, and 2 CMC, and commercial coating (corrosion inhibitor primer).</p>
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<p>Corrosion levels observed in the test specimens (TSs) coated with commercial paints before and after 15 days of exposure to critical atmospheric conditions simulated in the accelerated corrosion chamber. (1) TS before exposure; (2) TS coated with paint without biosurfactant; (3) TS coated with paint incorporating the biosurfactant. Paint A—formulated with polyacid-based resin, polyalcohols, drying oils, active pigments, additives, aliphatic solvent, and turpentine. Paint B—formulated with light hydrated petroleum distillates, xylene, toluene, cobalt octoate, manganese octoate, and methyl ethyl ketoxime. Paint C—formulated with oil-based resin, polyacids, polyalcohols, solvents, additives, and pigments.</p>
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<p>Mass losses detected in test specimens coated with commercial paints with and without biosurfactant (controls) before and after 15 days of exposure to critical atmospheric conditions simulated in the accelerated corrosion chamber. Paint A—formulated with polyacid-based resin, polyalcohols, drying oils, active pigments, additives, aliphatic solvent, and turpentine. Paint B—formulated with light hydrated petroleum distillates, xylene, toluene, cobalt octoate, manganese octoate, and methyl ethyl ketoxime. Paint C—formulated with oil-based resin, polyacids, polyalcohols, solvents, additives, and pigments.</p>
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33 pages, 45495 KiB  
Article
Peplospheric Influences on Local Greenhouse Gas and Aerosol Variability at the Lamezia Terme WMO/GAW Regional Station in Calabria, Southern Italy: A Multiparameter Investigation
by Francesco D’Amico, Claudia Roberta Calidonna, Ivano Ammoscato, Daniel Gullì, Luana Malacaria, Salvatore Sinopoli, Giorgia De Benedetto and Teresa Lo Feudo
Sustainability 2024, 16(23), 10175; https://doi.org/10.3390/su162310175 - 21 Nov 2024
Viewed by 502
Abstract
One of the keys towards sustainable policies and advanced air quality monitoring is the detailed assessment of all factors that affect the surface concentrations of greenhouse gases (GHGs) and aerosols. While the development of new atmospheric tracers can pinpoint emission sources, the atmosphere [...] Read more.
One of the keys towards sustainable policies and advanced air quality monitoring is the detailed assessment of all factors that affect the surface concentrations of greenhouse gases (GHGs) and aerosols. While the development of new atmospheric tracers can pinpoint emission sources, the atmosphere itself plays a relevant role even at local scales: Its dynamics can increase, or reduce, surface concentrations of pollutants harmful to human health and the environment. PBL (planetary boundary layer), or peplospheric, variability is known to affect such concentrations. In this study, an unprecedented characterization of PBL cycles and patterns is performed at the WMO/GAW regional coastal site of Lamezia Terme (code: LMT) in Calabria, Southern Italy, in conjunction with the analysis of key GHGs and aerosols. The analysis, accounting for five months of 2024 data, indicates that peplospheric variability and wind regimes influence the concentrations of key GHGs and aerosols. In particular, PBLH (PBL height) patterns have been tested to further influence the surface concentrations of carbon monoxide (CO), black carbon (BC), and particulate matter (PM). This research introduces four distinct wind regimes at LMT: breeze, not complete breeze, eastern synoptic, and western synoptic, each with its peculiar influences on the local transport of gases and aerosols. This research demonstrates that peplosphere monitoring needs to be considered when ensuring optimal air quality in urban and rural areas. Full article
(This article belongs to the Special Issue Sustainable Climate Action for Global Health)
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<p>(<b>A</b>) Modified Copernicus Digital Elevation Model [<a href="#B115-sustainability-16-10175" class="html-bibr">115</a>] of Europe, with a mark on LMT’s location. (<b>B</b>) Modified EMODnet [<a href="#B116-sustainability-16-10175" class="html-bibr">116</a>] highlighting LMT’s specific location in Southern Italy, within the region of Calabria. (<b>C</b>) Google Earth map, tilted by 70°, showing the observation site and key infrastructural/emission hotspots in the area. The “Highway” label indicates a point where the distance between LMT and the highway is ≈4.2 km. The “Lamezia Terme” label points to the town center. The “Station” label points to the busiest train station in the municipality of Lamezia Terme, the central one (<span class="html-italic">Lamezia Terme Centrale</span>).</p>
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<p>(<b>A</b>) Modified Copernicus Digital Elevation Model [<a href="#B115-sustainability-16-10175" class="html-bibr">115</a>] of Europe, with a mark on LMT’s location. (<b>B</b>) Modified EMODnet [<a href="#B116-sustainability-16-10175" class="html-bibr">116</a>] highlighting LMT’s specific location in Southern Italy, within the region of Calabria. (<b>C</b>) Google Earth map, tilted by 70°, showing the observation site and key infrastructural/emission hotspots in the area. The “Highway” label indicates a point where the distance between LMT and the highway is ≈4.2 km. The “Lamezia Terme” label points to the town center. The “Station” label points to the busiest train station in the municipality of Lamezia Terme, the central one (<span class="html-italic">Lamezia Terme Centrale</span>).</p>
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<p>Wind rose based on hourly data gathered during the observation period (1 May–30 September 2024). Calm refers to the reported instances (0%) of a wind speed of 0 m/s.</p>
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<p>Daily averages of GHG and aerosol parameters evaluated in this research study: (<b>A</b>) carbon monoxide (CO), in ppm (parts per million); (<b>B</b>) carbon dioxide (CO<sub>2</sub>), in ppm; (<b>C</b>) methane (CH<sub>4</sub>), in ppm; (<b>D</b>) equivalent black carbon (eBC), in μg/m<sup>3</sup>; and (<b>E</b>) particulate matter (PM) in μg/m<sup>3</sup>, divided into the size ranges PM<sub>1</sub>, PM<sub>2.5</sub>, PM<sub>4</sub>, and PM<sub>10</sub>. The gaps in CO, CO<sub>2</sub>, and CH<sub>4</sub> data shown in A-B-C are due to maintenance issues that affected the Picarro G2401. Similarly, Thermo Scientific 5012 MAAP data gathering was also affected by maintenance, as shown by a gap.</p>
Full article ">Figure 3 Cont.
<p>Daily averages of GHG and aerosol parameters evaluated in this research study: (<b>A</b>) carbon monoxide (CO), in ppm (parts per million); (<b>B</b>) carbon dioxide (CO<sub>2</sub>), in ppm; (<b>C</b>) methane (CH<sub>4</sub>), in ppm; (<b>D</b>) equivalent black carbon (eBC), in μg/m<sup>3</sup>; and (<b>E</b>) particulate matter (PM) in μg/m<sup>3</sup>, divided into the size ranges PM<sub>1</sub>, PM<sub>2.5</sub>, PM<sub>4</sub>, and PM<sub>10</sub>. The gaps in CO, CO<sub>2</sub>, and CH<sub>4</sub> data shown in A-B-C are due to maintenance issues that affected the Picarro G2401. Similarly, Thermo Scientific 5012 MAAP data gathering was also affected by maintenance, as shown by a gap.</p>
Full article ">Figure 3 Cont.
<p>Daily averages of GHG and aerosol parameters evaluated in this research study: (<b>A</b>) carbon monoxide (CO), in ppm (parts per million); (<b>B</b>) carbon dioxide (CO<sub>2</sub>), in ppm; (<b>C</b>) methane (CH<sub>4</sub>), in ppm; (<b>D</b>) equivalent black carbon (eBC), in μg/m<sup>3</sup>; and (<b>E</b>) particulate matter (PM) in μg/m<sup>3</sup>, divided into the size ranges PM<sub>1</sub>, PM<sub>2.5</sub>, PM<sub>4</sub>, and PM<sub>10</sub>. The gaps in CO, CO<sub>2</sub>, and CH<sub>4</sub> data shown in A-B-C are due to maintenance issues that affected the Picarro G2401. Similarly, Thermo Scientific 5012 MAAP data gathering was also affected by maintenance, as shown by a gap.</p>
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<p>Daily averages of environmental and meteorological data: (<b>A</b>) solar radiation in W/m<sup>2</sup>; (<b>B</b>) temperature in Celsius degrees, °C; (<b>C</b>) relative humidity, as a percentage (%); (<b>D</b>) scattering, as Mm<sup>−1</sup>.</p>
Full article ">Figure 4 Cont.
<p>Daily averages of environmental and meteorological data: (<b>A</b>) solar radiation in W/m<sup>2</sup>; (<b>B</b>) temperature in Celsius degrees, °C; (<b>C</b>) relative humidity, as a percentage (%); (<b>D</b>) scattering, as Mm<sup>−1</sup>.</p>
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<p>Hourly averages of GHG and aerosol parameters evaluated in this research study: (<b>A</b>) carbon monoxide (CO), in ppm (parts per million); (<b>B</b>) carbon dioxide (CO<sub>2</sub>), in ppm; (<b>C</b>) methane (CH<sub>4</sub>), in ppm; (<b>D</b>) equivalent black carbon (eBC), in μg/m<sup>3</sup>; and (<b>E</b>) particulate matter (PM) in μg/m<sup>3</sup>, divided into the size ranges PM<sub>1</sub>, PM<sub>2.5</sub>, PM<sub>4</sub>, and PM<sub>10</sub>. 36 h moving averages of CO, CO<sub>2</sub>, CH<sub>4</sub> (pm), and eBC (μg/m<sup>3</sup>) are shown in cyan.</p>
Full article ">Figure 5 Cont.
<p>Hourly averages of GHG and aerosol parameters evaluated in this research study: (<b>A</b>) carbon monoxide (CO), in ppm (parts per million); (<b>B</b>) carbon dioxide (CO<sub>2</sub>), in ppm; (<b>C</b>) methane (CH<sub>4</sub>), in ppm; (<b>D</b>) equivalent black carbon (eBC), in μg/m<sup>3</sup>; and (<b>E</b>) particulate matter (PM) in μg/m<sup>3</sup>, divided into the size ranges PM<sub>1</sub>, PM<sub>2.5</sub>, PM<sub>4</sub>, and PM<sub>10</sub>. 36 h moving averages of CO, CO<sub>2</sub>, CH<sub>4</sub> (pm), and eBC (μg/m<sup>3</sup>) are shown in cyan.</p>
Full article ">Figure 5 Cont.
<p>Hourly averages of GHG and aerosol parameters evaluated in this research study: (<b>A</b>) carbon monoxide (CO), in ppm (parts per million); (<b>B</b>) carbon dioxide (CO<sub>2</sub>), in ppm; (<b>C</b>) methane (CH<sub>4</sub>), in ppm; (<b>D</b>) equivalent black carbon (eBC), in μg/m<sup>3</sup>; and (<b>E</b>) particulate matter (PM) in μg/m<sup>3</sup>, divided into the size ranges PM<sub>1</sub>, PM<sub>2.5</sub>, PM<sub>4</sub>, and PM<sub>10</sub>. 36 h moving averages of CO, CO<sub>2</sub>, CH<sub>4</sub> (pm), and eBC (μg/m<sup>3</sup>) are shown in cyan.</p>
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<p>Hourly averages of environmental and meteorological data: (<b>A</b>) temperature, in Celsius degrees, °C; (<b>B</b>) relative humidity, as a percentage (%); and (<b>C</b>) scattering, as Mm<sup>−1</sup>. 36 h moving averages of T (°C) and RH (%) are shown in dark red.</p>
Full article ">Figure 6 Cont.
<p>Hourly averages of environmental and meteorological data: (<b>A</b>) temperature, in Celsius degrees, °C; (<b>B</b>) relative humidity, as a percentage (%); and (<b>C</b>) scattering, as Mm<sup>−1</sup>. 36 h moving averages of T (°C) and RH (%) are shown in dark red.</p>
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<p>Daily cycles of GHG and aerosol parameters analyzed in this research study, divided by wind regime: (<b>A</b>) carbon monoxide (CO), in ppm (parts per million); (<b>B</b>) carbon dioxide (CO<sub>2</sub>), in ppm; (<b>C</b>) methane (CH<sub>4</sub>), in ppm; (<b>D</b>) equivalent black carbon (eBC), in μg/m<sup>3</sup>; (<b>E</b>) particulate matter (PM) in μg/m<sup>3</sup>, divided into the size ranges PM<sub>1</sub>, PM<sub>2.5</sub>, PM<sub>4</sub>, and PM<sub>10</sub> but not accounting for wind regime categories; (<b>F</b>) PM<sub>2.5</sub>, with wind regimes; and (<b>G</b>) PM<sub>10</sub>, with wind regimes. Where present, shaded areas refer to intervals within one standard deviation (±σ) from the reported values.</p>
Full article ">Figure 7 Cont.
<p>Daily cycles of GHG and aerosol parameters analyzed in this research study, divided by wind regime: (<b>A</b>) carbon monoxide (CO), in ppm (parts per million); (<b>B</b>) carbon dioxide (CO<sub>2</sub>), in ppm; (<b>C</b>) methane (CH<sub>4</sub>), in ppm; (<b>D</b>) equivalent black carbon (eBC), in μg/m<sup>3</sup>; (<b>E</b>) particulate matter (PM) in μg/m<sup>3</sup>, divided into the size ranges PM<sub>1</sub>, PM<sub>2.5</sub>, PM<sub>4</sub>, and PM<sub>10</sub> but not accounting for wind regime categories; (<b>F</b>) PM<sub>2.5</sub>, with wind regimes; and (<b>G</b>) PM<sub>10</sub>, with wind regimes. Where present, shaded areas refer to intervals within one standard deviation (±σ) from the reported values.</p>
Full article ">Figure 7 Cont.
<p>Daily cycles of GHG and aerosol parameters analyzed in this research study, divided by wind regime: (<b>A</b>) carbon monoxide (CO), in ppm (parts per million); (<b>B</b>) carbon dioxide (CO<sub>2</sub>), in ppm; (<b>C</b>) methane (CH<sub>4</sub>), in ppm; (<b>D</b>) equivalent black carbon (eBC), in μg/m<sup>3</sup>; (<b>E</b>) particulate matter (PM) in μg/m<sup>3</sup>, divided into the size ranges PM<sub>1</sub>, PM<sub>2.5</sub>, PM<sub>4</sub>, and PM<sub>10</sub> but not accounting for wind regime categories; (<b>F</b>) PM<sub>2.5</sub>, with wind regimes; and (<b>G</b>) PM<sub>10</sub>, with wind regimes. Where present, shaded areas refer to intervals within one standard deviation (±σ) from the reported values.</p>
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<p>Daily cycles of environmental and meteorological data: (<b>A</b>) solar radiation in W/m<sup>2</sup>; (<b>B</b>) temperature (°C); (<b>C</b>) relative humidity (%); and (<b>D</b>) scattering (Mm<sup>−1</sup>). Where present, shaded areas refer to intervals within one standard deviation (±σ) from the reported values.</p>
Full article ">Figure 8 Cont.
<p>Daily cycles of environmental and meteorological data: (<b>A</b>) solar radiation in W/m<sup>2</sup>; (<b>B</b>) temperature (°C); (<b>C</b>) relative humidity (%); and (<b>D</b>) scattering (Mm<sup>−1</sup>). Where present, shaded areas refer to intervals within one standard deviation (±σ) from the reported values.</p>
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<p>Percentile roses of GHGs and aerosols evaluated in this study. The radius of each rose shows concentrations, while the shaded areas represent the coverage rate by percentile range: (<b>A</b>) carbon monoxide (CO), (<b>B</b>) carbon dioxide (CO<sub>2</sub>), (<b>C</b>) methane (CH<sub>4</sub>), (<b>D</b>) equivalent black carbon (eBC), (<b>E</b>) total particulate matter (PM), (<b>F</b>) PM<sub>2.5</sub>, and (<b>G</b>) PM<sub>10</sub>.</p>
Full article ">Figure 9 Cont.
<p>Percentile roses of GHGs and aerosols evaluated in this study. The radius of each rose shows concentrations, while the shaded areas represent the coverage rate by percentile range: (<b>A</b>) carbon monoxide (CO), (<b>B</b>) carbon dioxide (CO<sub>2</sub>), (<b>C</b>) methane (CH<sub>4</sub>), (<b>D</b>) equivalent black carbon (eBC), (<b>E</b>) total particulate matter (PM), (<b>F</b>) PM<sub>2.5</sub>, and (<b>G</b>) PM<sub>10</sub>.</p>
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<p>Daily (<b>A</b>) and hourly (<b>B</b>) averages of PBLH at LMT. Daily cycle (<b>C</b>) divided by the four wind regime categories described in <a href="#sec2dot2-sustainability-16-10175" class="html-sec">Section 2.2</a>. Where present, shaded areas refer to intervals within one standard deviation (±σ) from the reported values.</p>
Full article ">Figure 10 Cont.
<p>Daily (<b>A</b>) and hourly (<b>B</b>) averages of PBLH at LMT. Daily cycle (<b>C</b>) divided by the four wind regime categories described in <a href="#sec2dot2-sustainability-16-10175" class="html-sec">Section 2.2</a>. Where present, shaded areas refer to intervals within one standard deviation (±σ) from the reported values.</p>
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<p>Temporal variation in ceilometer backscattered profiles, aggregated on a 5 min basis, during select days with synoptic flows from west (1, 2 May) and east (14, 15 May), well-developed breeze (11, 12 August), and not complete breeze (17, 18 July). Yellow contours underline PBL boundaries, while turquoise and green contours indicate cloudy layers.</p>
Full article ">Figure 11 Cont.
<p>Temporal variation in ceilometer backscattered profiles, aggregated on a 5 min basis, during select days with synoptic flows from west (1, 2 May) and east (14, 15 May), well-developed breeze (11, 12 August), and not complete breeze (17, 18 July). Yellow contours underline PBL boundaries, while turquoise and green contours indicate cloudy layers.</p>
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<p>Scatter plots testing the correlation between PBLH and carbon monoxide (CO) under the four observed wind regimes (top: breeze and not complete breeze; bottom: western and eastern synoptic flows).</p>
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<p>Scatter plots testing the correlation between PBLH and carbon dioxide (CO<sub>2</sub>) under the four observed wind regimes (top: breeze and not complete breeze; bottom: western and eastern synoptic flows).</p>
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<p>Scatter plots testing the correlation between PBLH and methane (CH<sub>4</sub>) under the four observed wind regimes (top: breeze and not complete breeze; bottom: western and eastern synoptic flows).</p>
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<p>Scatter plots testing the correlation between PBLH and equivalent black carbon (eBC) under the four observed wind regimes (top: breeze and not complete breeze; bottom: western and eastern synoptic flows).</p>
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<p>Scatter plots testing the correlation between PBLH and PM<sub>2.5</sub> under the four observed wind regimes (top: breeze and not complete breeze; bottom: western and eastern synoptic flows).</p>
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<p>Scatter plots testing the correlation between PBLH and PM<sub>10</sub> under the four observed wind regimes (top: breeze and not complete breeze; bottom: western and eastern synoptic flows).</p>
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17 pages, 3996 KiB  
Article
The Influence of Relative Humidity and Pollution on the Meteorological Optical Range During Rainy and Dry Months in Mexico City
by Blanca Adilen Miranda-Claudes and Guillermo Montero-Martínez
Atmosphere 2024, 15(11), 1382; https://doi.org/10.3390/atmos15111382 - 16 Nov 2024
Viewed by 501
Abstract
The Meteorological Optical Range (MOR) is a measurement of atmospheric visibility. Visibility impairment has been linked to increased aerosol levels in the air. This study conducted statistical analyses using meteorological, air pollutant concentration, and MOR data collected in Mexico City from [...] Read more.
The Meteorological Optical Range (MOR) is a measurement of atmospheric visibility. Visibility impairment has been linked to increased aerosol levels in the air. This study conducted statistical analyses using meteorological, air pollutant concentration, and MOR data collected in Mexico City from August 2014 to December 2015 to determine the factors contributing to haze occurrence (periods when MOR < 10,000 m), defined using a light scatter sensor (PWS100). The outcomes revealed seasonal patterns in PM2.5 and relative humidity (RH) for haze occurrence along the year. PM2.5 levels during hazy periods in the dry season were higher compared to the wet season, aligning with periods of poor air quality (PM2.5 > 45 μg/m3). Pollutant-to-CO ratios suggested that secondary aerosols’ production, led by SO2 conversion to sulfate particles, mainly impacts haze occurrence during the dry season. Meanwhile, during the rainy season, the PWS100 registered haze events even with PM2.5 values close to 15 μg/m3 (considered good air quality). The broadened distribution of extinction efficiency during the wet period and its correlation with RH suggest that aerosol water vapor uptake significantly impacts visibility during this season. Therefore, attributing poor visibility strictly to poor air quality may not be appropriate for all times and locations. Full article
(This article belongs to the Section Meteorology)
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Figure 1

Figure 1
<p>The research methodology overview. Blue boxes represent the main phases/sections of the study, green boxes represent how the analysis was carried out, and the yellow box leads to the discussion of results.</p>
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<p>Time series for Meteorological Optical Range (<span class="html-italic">MOR</span>, black lines), meteorological, and pollutant (PM<sub>2.5</sub>, NO<sub>x</sub>, SO<sub>2</sub>, and CO) measurements from 22 to 23 November 2015. <span class="html-italic">MOR</span> data show a haze event on 23 November 2015. The upper panel (<b>a</b>) shows a comparison between PM<sub>2.5</sub>, NO<sub>x</sub>, and <span class="html-italic">RH</span> (red, blue, and yellow lines, respectively) measurements correlated with <span class="html-italic">MOR</span> data. The bottom panel (<b>b</b>) displays the SO<sub>2</sub>, CO, and <span class="html-italic">WS</span> (orange, blue, and green lines, respectively) estimates during the same period. It is observed that pollutant concentrations show higher levels during the haze occurrence. See more details in the text.</p>
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<p>The correlation matrix showing the relationship between <span class="html-italic">MOR</span> and meteorological and pollutants variables. Bold numbers in the green-colored cells indicate statistically significant results.</p>
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<p>The series of monthly averages of <span class="html-italic">MOR</span>, meteorological, and pollutant measurements obtained for haze (orange) and control (blue) periods. The information is displayed for the months when haze events occurred, so November 2014 and January, March, and October 2015 are missing. The open symbols indicate results obtained for the dry season. Each subfigure shows the comparison for the variables as: (<b>a</b>) <span class="html-italic">MOR</span>, (<b>b</b>) PM<sub>2.5</sub>, (<b>c</b>) <span class="html-italic">RH</span>, (<b>d</b>) NO<sub>x</sub>, (<b>e</b>) <span class="html-italic">WS</span>, (<b>f</b>) SO<sub>2</sub>, and (<b>g</b>) <span class="html-italic">WDIR</span>.</p>
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<p>The dispersion of <span class="html-italic">MOR</span> values, categorized into haze (<span class="html-italic">MOR</span> &lt; 10,000 m, blue points) and non-haze (<span class="html-italic">MOR</span> &gt; 10,000 m, orange points) classes, as a function of <span class="html-italic">RH</span> and PM<sub>2.5</sub> for the dry (<b>left panel</b>) and the precipitating (<b>right panel</b>) seasons.</p>
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<p>The contribution of particulate (PM<sub>2.5</sub>) pollution levels in four visibility ranges during the two chosen precipitation periods. The upper panel shows that bad air quality conditions contribute significantly (up to 60%) to haze occurrence during the low precipitation period.</p>
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<p>Estimates of (<b>a</b>) PM<sub>2.5</sub>/CO (μg/m<sup>3</sup>/ppmv), (<b>b</b>) SO<sub>2</sub>/CO (ppbv/ppmv), and (<b>c</b>) NO<sub>x</sub>/CO (ppbv/ppmv) ratios for two <span class="html-italic">MOR</span> ranges (shown in the <span class="html-italic">x</span>-axis of the bottom panel). Orange and blue bars show the mean values for each ratio during the representative periods of haze and good <span class="html-italic">MOR</span> estimates, respectively. The vertical bars correspond to the standard deviation of the mean values. Under different visibility conditions, these ratios are useful as a proxy for the contribution of gas–particle conversion processes. See details in the text.</p>
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<p>Frequency distributions of the extinction capacity of PM<sub>2.5</sub> per unit mass under diverse <span class="html-italic">RH</span> ranges: (<b>a</b>) 40 % &lt; <span class="html-italic">RH</span> &lt; 60 %, (<b>b</b>) 60 % &lt; <span class="html-italic">RH</span> &lt; 80 %, and (<b>c</b>) 80 % ≤ <span class="html-italic">RH.</span> The obtained distributions are displayed for the dry and rainy seasons.</p>
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<p>Cumulative curves of haze periods as a function of the PM<sub>2.5</sub> levels (<b>a</b>) and <span class="html-italic">RH</span> (<b>b</b>) during the two chosen seasons. The 50% frequency level was used to determine the particulate and moisture threshold values for haze incidence at the sampling site during the rainy and low precipitation seasons.</p>
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10 pages, 5129 KiB  
Commentary
Challenging the Chemistry of Climate Change
by Bruce Peachey and Nobuo Maeda
Chemistry 2024, 6(6), 1439-1448; https://doi.org/10.3390/chemistry6060086 - 16 Nov 2024
Viewed by 4083
Abstract
As talk grows about billions or even trillions of dollars being directed toward potential “Net Zero” activities, it is imperative that the chemistry inherent in or driving those actions make scientific sense. The challenge is to close the mass and energy balances to [...] Read more.
As talk grows about billions or even trillions of dollars being directed toward potential “Net Zero” activities, it is imperative that the chemistry inherent in or driving those actions make scientific sense. The challenge is to close the mass and energy balances to the carbon and oxygen cycles in the Earth’s atmosphere and oceans. Several areas of climate science have been identified that chemists can investigate through methods that do not require a supercomputer or a climate model for investigation, most notably the following: (1) The carbon cycle, which still needs to be balanced, as many known streams, such as carbon to landfills, carbon in human-enhanced sewage and land runoff streams, and carbon stored in homes and other material, do not seem to have been accounted for in carbon balances used by the IPCC. (2) Ocean chemistry and balances are required to explain the causes of regional and local-scale salinity, pH, and anoxic conditions vs. global changes. For example, local anoxic conditions are known to be impacted by changes in nutrient discharges to oceans, while large-scale human diversions of fresh water streams for irrigation, power, and industrial cooling must have regional impacts on oceanic salinity and pH. (3) Carbon Capture and Storage (CCS) schemes, if adopted on the large scales being proposed (100s to 1000s of Gt net injection by 2100), should impact the composition of the atmosphere by reducing free oxygen, adding more water from combustion, and displacing saline water from subsurface aquifers. Data indicate that atmospheric oxygen is currently dropping at about twice the rate of CO2 concentrations increasing, which is consistent with combustion chemistry with 1.5 to 2 molecules of oxygen being converted through combustion to 1 molecule of CO2 and 1 to 2 molecules of H2O, with reverse reactions occurring as a result of oxygenic photosynthesis by increased plant growth. The CCS schemes will sabotage these reverse reactions of oxygenic photosynthesis by permanently sequestering the oxygen atoms in each CO2 molecule. Full article
(This article belongs to the Section Physical Chemistry and Chemical Physics)
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Figure 1
<p>Atmospheric CO<sub>2</sub> concentrations over geologic time range of 0–7000 ppmv (left image, reproduced from Ref. [<a href="#B9-chemistry-06-00086" class="html-bibr">9</a>]) and recent measurement range of 310–430 ppm (right image, reproduced from NOAA <a href="https://gml.noaa.gov/ccgg/trends/" target="_blank">https://gml.noaa.gov/ccgg/trends/</a> (accessed on 30 September 2024). The (<b>left</b>) panel shows that the atmospheric CO<sub>2</sub> concentration has varied considerably over time while the temperature has been falling steadily over the last 450 million years, which illustrates the difficulty in directly correlating CO<sub>2</sub> as being a driver of temperature. The (<b>right</b>) panel shows the steadily rising atmospheric CO<sub>2</sub> concentrations over the last 65 years, which are still at much lower concentrations than indicated by CO<sub>2</sub> proxies.</p>
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<p>Graph illustrating the impacts of carbon sinks on CO<sub>2</sub> buildup in the atmosphere (reproduced from [<a href="#B12-chemistry-06-00086" class="html-bibr">12</a>]). The atmospheric CO<sub>2</sub> concentration growth remained below the anthropogenic CO<sub>2</sub> emissions over the years because a fraction of the anthropogenic CO<sub>2</sub> emissions has been absorbed by natural or human-caused carbon sinks. As time went by, the anthropogenic CO<sub>2</sub> emissions increased/accelerated, but so did the absorption by the less-defined carbon sinks. This implies that to predict future change, a better understanding is needed of where the additional carbon added has gone and whether this has a net positive or negative effect.</p>
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<p>This diagram of the fast carbon cycle shows the movement of carbon between the land, atmosphere, and oceans. White numbers indicate stored carbon (stocks). Yellow numbers are natural fluxes (flows), and red is assumed human contributions in gigatons of carbon per year and assumed carbon masses moving into assumed sinks (adapted from <a href="https://earthobservatory.nasa.gov/features/CarbonCycle" target="_blank">https://earthobservatory.nasa.gov/features/CarbonCycle</a> (accessed on 30 September 2024). Blue arrows and boxes have been added by the authors to indicate carbon streams not shown in the original reference diagram. Focusing on the red numbers would show that an incremental 3Gt/yr of carbon is going to increased plant biomass or soil carbon, but the diagram does not split this out or show the impact of other human activities, which would remove and sequester that carbon. Similarly, 2 Gt/yr of carbon is shown going into the oceans with nothing returning, but the diagram does not specify if that carbon is in the form of CO<sub>2</sub>, which might cause acidification, or carbon, which may just increase sedimentation in the oceans.</p>
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<p>The change in the composition of the Earth’s atmosphere (left image, reproduced from Ref. [<a href="#B18-chemistry-06-00086" class="html-bibr">18</a>]) and the oxygen concentration in the Earth’s atmosphere over time (right image, reproduced from Ref. [<a href="#B19-chemistry-06-00086" class="html-bibr">19</a>]). The original atmosphere of the Earth contained very little free oxygen. All the oxygen in the atmosphere now came from oxygenic photosynthesis of plants over billions of years. While oxygen is currently a major component of the atmosphere, there are areas where anoxic conditions may be impacted and need to be better understood in the context of the past and potential future.</p>
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<p>Measured data on CO<sub>2</sub> and O<sub>2</sub> concentrations between 1991 and 2020 with correlations (reproduced from Ref. [<a href="#B21-chemistry-06-00086" class="html-bibr">21</a>]). The O<sub>2</sub> concentrations have been dropping by ~130 ppm, while the CO<sub>2</sub> concentrations have been increasing by about 50 ppm over 20 years. What does this potentially tell us about the availability of CO<sub>2</sub> for ocean acidification vs. the transfer of carbon to ocean sediments?</p>
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<p>Relative changes in the type and amount of fossil fuel consumption over time (reproduced from BP Statistical Review of World Energy 2019). The fuel consumption by humans has consistently been shifting from carbon-rich sources to progressively hydrogen-rich ones. The combustion of these fuels should have changed the relationship between the rate of CO<sub>2</sub> increase vs. the rate of O<sub>2</sub> decrease in the atmosphere in recent decades.</p>
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15 pages, 4484 KiB  
Article
Predicting Wheat Potential Yield in China Based on Eco-Evolutionary Optimality Principles
by Shen Tan, Shengchao Qiao, Han Wang and Sheng Chang
Agriculture 2024, 14(11), 2058; https://doi.org/10.3390/agriculture14112058 - 15 Nov 2024
Viewed by 537
Abstract
Accurately predicting the wheat potential yield (PY) is crucial for enhancing agricultural management and improving resilience to climate change. However, most existing crop models for wheat PY rely on type-specific parameters that describe wheat traits, which often require calibration and, in turn, reduce [...] Read more.
Accurately predicting the wheat potential yield (PY) is crucial for enhancing agricultural management and improving resilience to climate change. However, most existing crop models for wheat PY rely on type-specific parameters that describe wheat traits, which often require calibration and, in turn, reduce prediction confidence when applied across different spatial or temporal scales. In this study, we integrated eco-evolutionary optimality (EEO) principles with a universal productivity model, the Pmodel, to propose a comprehensive full-chain method for predicting wheat PY. Using this approach, we forecasted wheat PY across China under typical shared socioeconomic pathways (SSPs). Our findings highlight the following: (1) Incorporating EEO theory improves PY prediction performance compared to current parameter-based crop models. (2) In the absence of phenological responses, rising atmospheric CO2 concentrations universally benefit wheat growth and PY, while increasing temperatures have predominantly negative effects across most regions. (3) Warmer temperatures expand the window for selecting sowing dates, leading to a national trend toward earlier sowing. (4) By simultaneously considering climate impacts on wheat growth and sowing dates, we predict that PY in China’s main producing regions will significantly increase from 2020 to 2060 and remain stable under SSP126. However, under SSP370, while there is no significant trend in PY during 2020–2060, increases are expected thereafter. These results provide valuable insights for policymakers navigating the complexities of climate change and optimizing wheat production to ensure food security. Full article
(This article belongs to the Section Ecosystem, Environment and Climate Change in Agriculture)
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Figure 1

Figure 1
<p>Map of cultivated wheat area proportion in China. The black points represent the wheat farmland in this grid that is mainly irrigated.</p>
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<p>Workflow for predicting wheat PY based on the EEO theory. In the method block, three major methods are in bold and will be introduced in the following sections. The results of all experiments will be demonstrated in the corresponding sections.</p>
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<p>Comparison of wheat PY prediction maps from various sources against EARTHSTAT (<b>a</b>). In addition to the typical crop models shown in panel (<b>b</b>), other models include (<b>c</b>) CLMcrop, (<b>d</b>) EpicBoku, (<b>e</b>) EpicIIASA, (<b>f</b>) EpicTAMU, (<b>g</b>) Gepic, and (<b>h</b>) ORCHIDEE-crop. MAE and RMSE are calculated after masking nonwheat grids. The units for both MAE and RMSE are tons per hectare.</p>
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<p>PY frequency comparison of EARTHSTAT, this study, and ensembled results of other crop models. The shade of model ensemble represents the 95% confidence interval of different model results.</p>
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<p>Wheat PY prediction considering the response to the climate change (with static sowing date). (<b>a</b>,<b>b</b>) represent the PY variation from 2021 to 2060 and 2061 to 2100 under SSP 126, respectively; (<b>c</b>,<b>d</b>) represent the PY variation from 2021 to 2060 and 2061 to 2100 under SSP 370, respectively. The grid with significant variation trend is labeled with the black points.</p>
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<p>Prediction of optimized wheat sowing date. (<b>a</b>,<b>b</b>) represent the sowing date variation from 2021 to 2060 and 2061 to 2100 under SSP 126, respectively; (<b>c</b>,<b>d</b>) represent the sowing date variation from 2021 to 2060 and 2061 to 2100 under SSP 370, respectively. The grid with significant variation trend is labeled with the black points. A positive value in this figure represents an advance of the sowing date.</p>
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<p>Prediction for relative variation of total wheat PY in China. We use the average PY during 2011 to 2020 as the benchmark. Dashed line represents the annual wheat PY, thick line represents the PY trend after smoothing. Two simulation configurations, with and without the optimizing sowing date, are represented by two colors.</p>
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<p>Prediction for wheat PY in China. (<b>a</b>,<b>b</b>) represent the PY variation from 2021 to 2060 and 2061 to 2100 under SSP 126, respectively; (<b>c</b>,<b>d</b>) represent the PY variation from 2021 to 2060 and 2061 to 2100 under SSP 370, respectively. The grid with significant variation trend is labeled with the black points.</p>
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