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Search Results (3,442)

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24 pages, 9689 KiB  
Article
Genome-Wide Identification, Evolution, and Expression Analysis of the Dirigent Gene Family in Cassava (Manihot esculenta Crantz)
by Mingchao Li, Kai Luo, Wenke Zhang, Man Liu, Yunfei Zhang, Huling Huang, Yinhua Chen, Shugao Fan and Rui Zhang
Agronomy 2024, 14(8), 1758; https://doi.org/10.3390/agronomy14081758 (registering DOI) - 11 Aug 2024
Abstract
Dirigent (DIR) genes play a pivotal role in plant development and stress adaptation. Manihot esculenta Crantz, commonly known as cassava, is a drought-resistant plant thriving in tropical and subtropical areas. It is extensively utilized for starch production, bioethanol, and animal feed. [...] Read more.
Dirigent (DIR) genes play a pivotal role in plant development and stress adaptation. Manihot esculenta Crantz, commonly known as cassava, is a drought-resistant plant thriving in tropical and subtropical areas. It is extensively utilized for starch production, bioethanol, and animal feed. However, a comprehensive analysis of the DIR family genes remains unexplored in cassava, a crucial cash and forage crop in tropical and subtropical regions. In this study, we characterize a total of 26 cassava DIRs (MeDIRs) within the cassava genome, revealing their uneven distribution across 13 of the 18 chromosomes. Phylogenetic analysis classified these genes into four subfamilies: DIR-a, DIR-b/d, DIR-c, and DIR-e. Comparative synteny analysis with cassava and seven other plant species (Arabidopsis (Arabidopsis thaliana), poplar (Populus trichocarpa), soybean (Glycine max), tomato (Solanum lycopersicum), rice (Oryza sativa), maize (Zea mays), and wheat (Triticum aestivum)) provided insights into their likely evolution. We also predict protein interaction networks and identify cis-acting elements, elucidating the functional differences in MeDIR genes. Notably, MeDIR genes exhibited specific expression patterns across different tissues and in response to various abiotic and biotic stressors, such as pathogenic bacteria, cadmium chloride (CdCl2), and atrazine. Further validation through quantitative real-time PCR (qRT-PCR) confirmed the response of DIR genes to osmotic and salt stress. These findings offer a comprehensive resource for understanding the characteristics and biological functions of MeDIR genes in cassava, enhancing our knowledge of plant stress adaptation mechanisms. Full article
16 pages, 2251 KiB  
Article
Sources of the Trace Metals Contaminating Soils in Recreational Forest and Glade Areas in Krakow, a Large City in Southern Poland
by Katarzyna Solek-Podwika and Krystyna Ciarkowska
Sustainability 2024, 16(16), 6874; https://doi.org/10.3390/su16166874 (registering DOI) - 10 Aug 2024
Viewed by 205
Abstract
Soil pollution mainly results from particulate matter falling from the atmosphere; for example, PM10 and PM2.5 originate from anthropogenic sources. Krakow is both an industrial and touristic city. The aim of this research was to establish the sources and find the main drivers [...] Read more.
Soil pollution mainly results from particulate matter falling from the atmosphere; for example, PM10 and PM2.5 originate from anthropogenic sources. Krakow is both an industrial and touristic city. The aim of this research was to establish the sources and find the main drivers of trace metal (TM) soil contamination in the recreational city park in Krakow. This study was performed on forest soils and glades located near built-up areas and 100 m above built-up areas. The contents of lead, cadmium, zinc, chromium, organic carbon, total nitrogen, available nutrients, dehydrogenases, urease, and invertase activities in the soils were determined. Geo-accumulation, pollution load, Nemerov pollution indices, and potential ecological risk were calculated. Our results indicated low emissions (house heating and traffic) as the main sources of pollution. TM pollution was higher in the soils of built-up areas than in soils located 100 m above built-up areas, and forest soils were more polluted with TMs than glade soils. Activities undertaken as part of the sustainable development of the city should aim to reduce low emissions. Full article
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<p>Location of the research area (Krakow, Malopolska region) and research sites from which soil samples were taken.</p>
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<p>(<b>A</b>–<b>C</b>) Classed post maps showing distribution of mean pH values in KCl (<b>A</b>), SOM contents (<b>B</b>), and DHA activity (<b>C</b>) in the surface layers of soils collected from the Wolski Forest (built-up and green areas).</p>
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<p>SQe calculated as the geometrical mean of DHA, URE, and INW (<b>A</b>). Pollution indices: PiNemerov (<b>B</b>), ecological RI (<b>C</b>) for soils grouped according to location and plant cover. FW—forest soils from green areas, FT—forest soils from built-up areas, GW—glade soils from green areas, GT—glade soils from built-up areas in the 0–10- and 10–30 cm layers. Different letters (a–d) show statistically significant differences between mean values of the parameters among soils of different plant cover (α ≤ 0.05).</p>
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<p>SQe calculated as the geometrical mean of DHA, URE, and INW (<b>A</b>). Pollution indices: PiNemerov (<b>B</b>), ecological RI (<b>C</b>) for soils grouped according to location and plant cover. FW—forest soils from green areas, FT—forest soils from built-up areas, GW—glade soils from green areas, GT—glade soils from built-up areas in the 0–10- and 10–30 cm layers. Different letters (a–d) show statistically significant differences between mean values of the parameters among soils of different plant cover (α ≤ 0.05).</p>
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<p>(<b>A</b>–<b>D</b>) Classed post maps showing distribution of contents of Pb, Zn, Cd, and Cr in surface layers of soils collected in the Wolski Forest (built-up and green areas).</p>
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<p>PCA results showing the relationship between the studied variables (pH, Hh, SOM, N, K, P, Mg, DHA, URE, INW, Cd, Pb, Cr, and Zn) and the location and plant cover of the soils in the surface layer. FW—forest soils from green areas, FT—forest soils from built-up areas, GW—glade soils from green areas, GT—glade soils from built-up areas in the 0–10 cm layer.</p>
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18 pages, 23890 KiB  
Article
Exploration of Response Mechanisms in the Gills of Pacific Oyster (Crassostrea gigas) to Cadmium Exposure through Integrative Metabolomic and Transcriptomic Analyses
by Luyao Dong, Yanan Sun, Muyang Chu, Yuxin Xie, Pinyi Wang, Bin Li, Zan Li, Xiaohui Xu, Yanwei Feng, Guohua Sun, Zhongping Wang, Cuiju Cui, Weijun Wang and Jianmin Yang
Animals 2024, 14(16), 2318; https://doi.org/10.3390/ani14162318 (registering DOI) - 9 Aug 2024
Viewed by 181
Abstract
Marine mollusks, including oysters, are highly tolerant to high levels of cadmium (Cd), but the molecular mechanisms underlying their molecular response to acute Cd exposure remain unclear. In this study, the Pacific oyster Crassostrea gigas was used as a biological model, exposed to [...] Read more.
Marine mollusks, including oysters, are highly tolerant to high levels of cadmium (Cd), but the molecular mechanisms underlying their molecular response to acute Cd exposure remain unclear. In this study, the Pacific oyster Crassostrea gigas was used as a biological model, exposed to acute Cd stress for 96 h. Transcriptomic analyses of their gills were performed, and metabolomic analyses further validated these results. In our study, a total of 111 differentially expressed metabolites (DEMs) and 2108 differentially expressed genes (DEGs) were identified under acute Cd exposure. Further analyses revealed alterations in key genes and metabolic pathways associated with heavy metal stress response. Cd exposure triggered physiological and metabolic responses in oysters, including enhanced oxidative stress and disturbances in energy metabolism, and these changes revealed the biological response of oysters to acute Cd stress. Moreover, oysters could effectively enhance the tolerance and detoxification ability to acute Cd exposure through activating ABC transporters, enhancing glutathione metabolism and sulfur relay system in gill cells, and regulating energy metabolism. This study reveals the molecular mechanism of acute Cd stress in oysters and explores the molecular mechanism of high tolerance to Cd in oysters by using combined metabolomics and transcriptome analysis. Full article
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<p>Biochemical alterations of the acute Cd exposure <span class="html-italic">C. gigas</span>. (<b>a</b>) Increased intracellular Cd level in Cd-exposed oyster individuals. The bar chart depicts mean levels and standard deviation (SD) values, with <span class="html-italic">n</span> = 3. Significance differences were determined by <span class="html-italic">t</span>-test (<span class="html-italic">p</span> &lt; 0.05), denoted by asterisks (<b>*</b>). (<b>b</b>) The survival rate of oysters after 96 h of acute Cd exposure. (<b>c</b>–<b>f</b>) After Cd exposure, oxidative stress markers such as SOD (<b>c</b>), CAT (<b>d</b>), MDA (<b>e</b>), and GPx (<b>f</b>) were measured. Data were presented as the mean ± SD (<span class="html-italic">n</span> = 3). Distinguishing letters were assigned to indicate significant differences (<span class="html-italic">p</span> &lt; 0.05). Star plots depict the impact of Cd exposure on gill samples.</p>
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<p>Analysis of oyster transcriptome following a 96-hour exposure to Cd. (<b>a</b>) A volcano plot of DEGs is graphically represented with upregulated genes in red and downregulated genes in blue. (<b>b</b>) Hierarchical clustering based on the DEGs, where red signifies upregulation and blue signifies downregulation. (<b>c</b>) Enrichment of DEGs in GO terms categorized into cellular components, biological processes, and molecular functions. (<b>d</b>) KEGG pathway enrichment analysis of DEGs, with colors indicating <span class="html-italic">p</span>-value significance and bubble size reflecting the count of enriched genes.</p>
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<p>Analysis of oyster metabolomes following a 96-hour exposure to Cd. (<b>a</b>) OPLS-DA score plot of the metabolomic data. (<b>b</b>) PLS-DA sorting test plot of the metabolomic data. (<b>c</b>) Hierarchical clustering was performed using 111 DEMs, with red indicating upregulation and blue representing downregulation, respectively. (<b>d</b>) Sample comparisons for the matchstick diagram. The top 20 metabolites of up and down are displayed in the matchstick diagram. The <span class="html-italic">x</span>-axis of the matchstick diagram represents log<sub>2</sub> (Fold Change) values, the <span class="html-italic">y</span>-axis represents metabolites, and the size of the points corresponds to VIP values. The metabolites that are upregulated and downregulated are represented by the red and blue points, respectively.</p>
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<p>Pathway analysis of the DEMs. (<b>a</b>) Top 20 KEGG pathway results. <span class="html-italic">p</span>-values are represented by colors, while pathway impact is indicated by the size of the bubbles. (<b>b</b>) KEGG regulatory network diagram. Red circles represent individual metabolic pathways, yellow circles depict enzyme information related to specific substances, green circles indicate background substances for a metabolic pathway, purple circles represent information on molecular modules of a certain substance category, blue circles represent chemical interactions involving a specific substance, and green squares denote differentially expressed substances identified in this comparison.</p>
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<p>Correlation heatmap analysis of DEGs and DEMs. The DEMs are depicted on the <span class="html-italic">y</span>-axis, while the <span class="html-italic">x</span>-axis displays the DEGs. A correlation coefficient less than 0 is indicative of a negative correlation, and a coefficient greater than 0 indicates a positive correlation. Negative correlations are symbolized by the color blue, while positive correlations are represented by the color red.</p>
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<p>Pathway enrichment analysis of DEGs and DEMs. (<b>a</b>) Bubble plot of KEGG enrichment for DEGs and DEMs. The x-axis represents the ratio of the number of enriched differential metabolites or genes annotated to metabolites or genes in the pathway to the total number in that pathway (ratio). The <span class="html-italic">y</span>-axis represents KEGG pathways jointly enriched in the metabolome and transcriptome. The count indicates the number of enriched metabolites or genes in the pathway. The colors represent <span class="html-italic">p</span>-values, with brighter colors indicating smaller <span class="html-italic">p</span>-values and more significant pathway enrichment. (<b>b</b>) iPath pathway map of shared enriched pathways. Colored boxes represent enriched pathways, nodes depict various biochemical molecules, lines represent biochemical reactions, and blue lines within the pathways indicate pathways jointly enriched with DEGs and DEMs.</p>
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<p>Main biological pathway responses to acute Cd exposure in oysters. The blue boxes represent four core Cd exposure response pathways. The orange boxes represent DEMs associated with the main pathways. The green boxes represent downregulated DEGs related to the main pathways. The red elliptical frames represent upregulated DEGs associated with the main pathways.</p>
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16 pages, 1860 KiB  
Article
Associations between Non-Essential Trace Elements in Women’s Biofluids and IVF Outcomes in Euploid Single-Embryo Transfer Cycles
by Roberto Gonzalez-Martin, Andrea Palomar, Silvia Perez-Deben, Stefania Salsano, Alicia Quiñonero, Laura Caracena, Isabel Rucandio, Rocio Fernandez-Saavedra, Rodolfo Fernandez-Martinez, Estefania Conde-Vilda, Alberto J. Quejido, Juan Giles, Carmen Vidal, Jose Bellver and Francisco Dominguez
J. Xenobiot. 2024, 14(3), 1093-1108; https://doi.org/10.3390/jox14030062 - 8 Aug 2024
Viewed by 191
Abstract
Previous studies have found inconsistent associations between heavy metals and metalloids (cadmium, lead, mercury, and arsenic), and reproductive outcomes. The biofluid concentrations of ten non-essential trace elements (Hg, Pb, As, Ba, Sr, Rb, Cs, Sn, Ni, and Co) were evaluated in 51 Spanish [...] Read more.
Previous studies have found inconsistent associations between heavy metals and metalloids (cadmium, lead, mercury, and arsenic), and reproductive outcomes. The biofluid concentrations of ten non-essential trace elements (Hg, Pb, As, Ba, Sr, Rb, Cs, Sn, Ni, and Co) were evaluated in 51 Spanish women undergoing ICSI, PGT-A, and SET/FET. Nine out of ten non-essential elements were detectable in follicular fluid, whole blood, and urine collected the day of vaginal oocyte retrieval (VOR) and the day of embryo transfer and then analyzed by ICP-MS or Tricell DMA-80 for mercury. Elevated mercury and strontium concentrations in follicular fluid were associated with poor ovarian response and preimplantation outcomes. Worst preimplantation outcomes were also identified in women with elevated whole-blood strontium or mercury, urinary arsenic, barium, and tin the day of VOR. High concentrations of urinary rubidium on VOR day were linked with enhanced fertilization and blastocyst development. Excessive titanium in whole blood was associated with lower odds of implantation, clinical pregnancy, and achieving a live birth in a given IVF cycle. Excessive urinary arsenic on the day of embryo transfer was associated with lower odds of live birth. Although these preliminary results need to be confirmed in larger populations, distinguishing organic and inorganic element forms, our findings show that some non-essential elements have a detrimental impact on human IVF outcomes. Full article
(This article belongs to the Section Emerging Chemicals)
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<p>Forest plots representing the mean differences between the 20th and 80th percentiles (p20 vs. p80) (95% confidence interval) for ovarian response-related outcomes by non-essential trace element concentrations. The mean differences are presented for trigger day estradiol (E2) levels, oocyte yield, and the relative proportion of mature (MII) oocytes across the non-essential trace elements quantified in each biological matrix. Data were adjusted for age and BMI (both continuous). * <span class="html-italic">p</span> &lt; 0.05. ET, embryo transfer; VOR, vaginal oocyte retrieval.</p>
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<p>Forest plots representing the mean differences between the 20th and 80th percentiles (p20 vs. p80) (95% confidence interval) for preimplantation IVF outcomes by non-essential trace element concentrations. Mean differences are presented for the relative proportions of oocytes that were successfully fertilized, embryos developing to the blastocyst stage, and euploid blastocysts across the non-essential trace elements quantified in each biological matrix. Data were adjusted for age and BMI (both continuous). * <span class="html-italic">p</span> &lt; 0.05. ET, embryo transfer; VOR, vaginal oocyte retrieval.</p>
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<p>Forest plot representing the odds ratios (95% confidence interval) for clinical reproductive outcomes by non-essential trace element concentrations. The odds ratios are presented for embryo transfer, implantation, clinical pregnancy, live birth, and reproductive goal (achievement of a live birth in a given cycle) following single frozen euploid embryo transfer, across the non-essential trace elements levels quantified in each biological matrix. Data were adjusted for age and BMI (both continuous). In the case of urine obtained on the day of the embryo transfer, the probability of embryo transfer or reproductive success was not examined because it is not informative, since only women who underwent embryo transfer would be considered. * <span class="html-italic">p</span> &lt; 0.05. ET, embryo transfer; VOR, vaginal oocyte retrieval.</p>
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19 pages, 12499 KiB  
Article
Trace Elements Anomalous Concentrations in Building Materials—The Impact of Secondary Mineralisation Processes
by Agnieszka Pękala, Piotr Koszelnik, Michał Musiał and Tomasz Galek
Materials 2024, 17(16), 3909; https://doi.org/10.3390/ma17163909 - 7 Aug 2024
Viewed by 272
Abstract
The Pb, Cr, Cd, Ni, Zn, Cu, Co, As, Sr, Ba, and Zr content has been determined in the tested rock raw materials. The concentration of cadmium (Cd) was found to be elevated in all types of rock materials and was found on [...] Read more.
The Pb, Cr, Cd, Ni, Zn, Cu, Co, As, Sr, Ba, and Zr content has been determined in the tested rock raw materials. The concentration of cadmium (Cd) was found to be elevated in all types of rock materials and was found on average to be: 1.39 mg/kg in limestones, 0.86 mg/kg—sandstones, 0.44 mg/kg—diatomites, 0.55 mg/kg—opoka rocks, 0.89 mg/kg—marls, 0.21 mg/kg—gaizes 0.42 mg/kg—kaolin clays, and 2.13 mg/kg—decalcified opoka rocks. Higher concentrations of arsenic (As) have also been recorded in sandstones and diatomites, as well as lead (Pb) in limestones and sandstones. The results obtained indicate that the anomalous level of elements is of natural origin and the results of identified secondary mineralisation processes that have affected the tested materials. Pyritization and sulfatization processes have been detected. Mineralogical research has shown that these processes can be associated with the activity of biochemical processes caused by the decomposition of the soft tissues of animal organisms and the organic substances of plant origin that fill the stylolites. It has been shown that the content of strontium (Sr) increases in geologically older Jurassic formations compared to younger Cretaceous formations, which can be used in the monitoring of building materials. Full article
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Graphical abstract
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<p>Area of research carried out. Bełchatów lignite deposit (<b>A</b>) cross section through the Bełchatów lignite deposit [<a href="#B21-materials-17-03909" class="html-bibr">21</a>]; (<b>B</b>) location of the study area depicted in the colour composition of a Sentinel satellite image.</p>
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<p>Limestone microsections. Iron sulphides filling of oncoids (<b>a</b>) stylolite seams (<b>b</b>), (blue arrows).</p>
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<p>Lead (Pb) content in rock raw materials.</p>
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<p>Concentration of trace elements in clays.</p>
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<p>Cadmium (Cd) content in the rock raw materials studied.</p>
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<p>Arsenic (As) content in the rock raw materials studied.</p>
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<p>Concentration of trace elements in sandstones.</p>
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<p>Zirconium (Zr) content in the rock raw materials studied.</p>
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<p>Celestine crystal isolated from a crack in the outcrop. SEM/EDS research.</p>
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<p>Spectrum of celestine from limestone. EDS/BSE research.</p>
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<p>Iron sulphides filling the voids (<b>a</b>) stylolite seams (<b>b</b>) (markings: yellow arrows). Polarising microscope, 2P. (explanations: P-polariser).</p>
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<p>Organogenic limestone. Iron sulphides selectively fill organic remains. (<b>a</b>,<b>b</b>) carbonate sparite replaced by iron sulphides in ooids; (<b>c</b>,<b>d</b>) pyrite fills intracellular spaces in carbonate-type bioclasts. (<b>e</b>,<b>f</b>) selective replacement of carbonates with pyrite in bioclasts. Image of the polarising microscope 1P, 2P (explanations: P-polariser).</p>
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<p>Average strontium content (Sr) in rock raw materials.</p>
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<p>Distribution of strontium (Sr) in opoka rocks.</p>
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<p>Distribution of strontium (Sr) in limestones.</p>
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<p>Examples of Sr distribution profiles in the tested rock raw materials.</p>
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17 pages, 16669 KiB  
Article
Effects of Carbon-Based Modified Materials on Soil Water and Fertilizer Retention and Pollution Control in Rice Root Zone
by Wei Huang, Yangwen Jia, Cunwen Niu, Hexi Zhang, Yongtao Wang and Cheng Feng
Sustainability 2024, 16(16), 6750; https://doi.org/10.3390/su16166750 - 7 Aug 2024
Viewed by 696
Abstract
To seek an appropriate stabilization and remediation scheme for cadmium (Cd) and arsenic (As) pollution in farmland, a typical polluted soil sample was selected from a mining area in Southwest China for a soil box simulation experiment. Biochar (BC), a modified type of [...] Read more.
To seek an appropriate stabilization and remediation scheme for cadmium (Cd) and arsenic (As) pollution in farmland, a typical polluted soil sample was selected from a mining area in Southwest China for a soil box simulation experiment. Biochar (BC), a modified type of biochar made from rice husk with different mass ratios of ferric chloride and rice husk, was set up (the mass ratio of ferric chloride to rice husk was 1:9 (defined as LFB), 3:7 (defined as MFB), and 5:5 (defined as HFB) and the control group (BL)) to explore the effects of soil water and fertilizer loss, the bioavailability of Cd and As, and the bioenrichment effects of plant organs during the growth period of rice. The results showed that the porous structure and large specific surface area of biochar effectively regulated soil aggregate composition and improved soil water holding capacity. Compared to the BL treatment, soil water storage under the four carbon-based material control modes increased from 8.98% to 14.52%. Biochar has a strong ion exchangeability and can absorb soil ammonium, nitrogen, and phosphoric acid groups, effectively inhibiting the loss of soil fertilizer. Biochar improves soil pH and reduces the specific gravity of exchangeable Cd. In addition, the oxygen-containing functional groups in biochar can react with metals in a complex manner. The diethylenetriaminepentaacetic acid (DTPA) concentrations of Cd in soils treated with BC, LFB, MFB, and HFB were 79.69%, 72.92%, 64.58%, and 69.27% lower, respectively, than those treated with BL. In contrast, the Fe3+ in ferric chloride combines with As after hydrolysis and oxidation to form amorphous ferric arsenate precipitates or insoluble secondary minerals. Therefore, the curing effect of the modified biochar on As was more potent than that of applied biochar alone. In conclusion, ferric chloride-modified biochar can effectively inhibit the effects of water and fertilizer loss in farmland soil and realize cross-medium long-term inhibition and control of combined Cd and As pollution. Full article
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<p>Characteristics of soil water migration and diffusion. (<b>a</b>) Water storage at the seedling stage, (<b>b</b>) tillering water storage, (<b>c</b>) water storage at the jointing stage, (<b>d</b>) water storage during the pumping period, (<b>e</b>) water storage at maturity, and (<b>f</b>) soil water loss at different growth stages. In addition, a, b, ab, bc and c indicate that the parameters are significantly different under the same treatment (<span class="html-italic">p</span> &lt; 0.05). BL, BC, LFB, MFB and HFB represent the treatments set up in the research.</p>
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<p>Migration characteristics of nitrogen and phosphorus in soil. (<b>a</b>) Soil inorganic nitrogen at the seedling stage, (<b>b</b>) soil inorganic nitrogen at maturity, (<b>c</b>) soil inorganic nitrogen loss, (<b>d</b>) available soil phosphorus at the seedling stage, (<b>e</b>) available soil phosphorus at maturity, and (<b>f</b>) available soil phosphorus loss. In addition, a, b, ab, bc and c indicate that the parameters are significantly different under the same treatment (<span class="html-italic">p</span> &lt; 0.05). BL, BC, LFB, MFB and HFB represent the treatments set up in the research.</p>
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<p>Response relationship between soil water and fertilizer loss. (<b>a</b>) Response relationship between soil inorganic nitrogen and water loss and (<b>b</b>) response of available soil phosphorus to water loss. Note: Asterisks denote a significant difference between different treatments: * <span class="html-italic">p</span>  &lt;  0.05, ** <span class="html-italic">p</span>  &lt;  0.01 and *** <span class="html-italic">p</span>  &lt;  0.001.</p>
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<p>Bioavailability characteristics of heavy metals in soil. (<b>a</b>) DTPA extraction concentration of Cd and (<b>b</b>) DTPA extraction concentration of As. In addition, a, b, bc and c indicate that the parameters are significantly different under the same treatment (<span class="html-italic">p</span> &lt; 0.05). BL, BC, LFB, MFB and HFB represent the treatments set up in the research.</p>
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<p>Soil water characteristic curves. (<b>a</b>) Soil water retention characteristics at the seedling stage and (<b>b</b>) soil water retention characteristics at maturity.</p>
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<p>Soil cation exchange capacity. (<b>a</b>) Soil cation exchange capacity at the seedling stage and (<b>b</b>) soil cation exchange capacity at maturity. In addition, a, b, ab and c indicate that the parameters are significantly different under the same treatment (<span class="html-italic">p</span> &lt; 0.05). BL, BC, LFB, MFB and HFB represent the treatments set up in the research.</p>
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<p>Isothermal adsorption model of Cd and As on carbon-based materials. (<b>a</b>) Langmuir isothermal adsorption curve of Cd, (<b>b</b>) Freundlich isothermal adsorption curve of Cd, (<b>c</b>) Langmuir isothermal adsorption curve of As, and (<b>d</b>) Freundlich isothermal adsorption curve of As.</p>
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19 pages, 9905 KiB  
Article
Application of Crustaceans as Ecological Markers for the Assessment of Pollution of Brackish Lakes of Bulgaria Based on Their Ability to Accumulate the Heavy Metals Cd, Zn and Ni
by Elica Valkova, Vasil Atanasov, Margarita H. Marinova, Antoaneta Yordanova, Kristian Yakimov and Yordan Kutsarov
Limnol. Rev. 2024, 24(3), 282-300; https://doi.org/10.3390/limnolrev24030017 - 5 Aug 2024
Viewed by 325
Abstract
The present study aimed to assess the pollution of Bulgarian brackish lakes based on their ability to accumulate the heavy metals Cd, Zn and Ni. Physicochemical parameters, including pH, electrical conductivity and salinity of the waters, were determined by potentiometric methods. The heavy [...] Read more.
The present study aimed to assess the pollution of Bulgarian brackish lakes based on their ability to accumulate the heavy metals Cd, Zn and Ni. Physicochemical parameters, including pH, electrical conductivity and salinity of the waters, were determined by potentiometric methods. The heavy metal content of the water and crustacean samples was determined by atomic absorption spectrophotometry. The highest pH in the investigated lakes (Atanasovsko Lake, Poda and Pomorie Lake) in the period May–September 2021 was found in the month of September, in the waters of Atanasovsko Lake (8.84). The concentrations of Cd measured in Atanasovsko Lake in the fall were in the order of 0.0125 µg/L—the highest value recorded for all the studied water bodies. The concentrations of zinc and nickel in the waters did not exceed the norms in Bulgarian legislation. The dynamics of biogenic elements (Zn and Ni) in crustaceans were inversely proportional to those found in the waters. The levels of the toxicant cadmium as well as the metals zinc and nickel in the species Gammarus spp. and Atremia spp., inhabiting all analyzed water bodies, were significantly lower than those specified in the Bulgarian and European legislation. The pH and electrical conductivity parameters of the tested waters, as well as the concentrations of the heavy metals, cadmium, zinc and nickel, were within the recommended values. High positive correlations were determined between the content of nickel, on the one hand, and cadmium and zinc, on the other, in the organism of the investigated crustaceans. A longer period of research is needed to accurately determine the degree of contamination of these waters. Full article
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<p>Map of the studied area, including the sampling points located near the Bulgarian coast of the Black Sea.</p>
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<p>pH from the studied sampling points, which belong to type L9 (medium saline) and L10 (extremely saline) lakes. Norm—Regulation № H-4 of 14 September 2012 on the characterization of surface waters from the Bulgarian legislation.</p>
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<p>Electrical conductivity of the waters from the studied sampling points, which belong to lakes of type L9 (medium saline) and L10 (highly saline) lakes.</p>
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<p>Salinity of waters from the investigated sampling points, which fall into type L9 (medium saline) and L10 (extremely saline) lakes.</p>
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<p>Content of Cd in the waters of the studied sampling points, which fall into type L9 (medium saline) and L10 (highly saline) lakes. Norm—Regulation № H-4 of 14 September 2012 on the characterization of surface waters from the Bulgarian legislation.</p>
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<p>Content of Zn in the waters of the investigated sampling points, which belong to type L9 (medium saline) and L10 (extremely saline) lakes.</p>
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<p>Content of Ni in the waters of the investigated sampling points, which fall into type L9 (medium saline) and L10 (highly saline) lakes.</p>
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<p>Content of Cd in the organism of representatives of crustaceans (Branchiopoda: Anostraca and Malacostraca: Amphipoda) taken from the Atanasovsko Lake Maintained Reserve, Poda Protected Area and Pomorie Lake Protected Area.</p>
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<p>Content of Ni in the organism of representatives of crustaceans (Branchiopoda: Anostraca and Malacostraca: Amphipoda) sampled from the Atanasovsko Lake Nature Reserve, Poda Protected Area and Pomorie Lake Protected Area.</p>
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<p>Zn content of crustaceans (Branchiopoda: Anostraca and Malacostraca: Amphipoda) sampled from the Atanasovsko Lake Maintained Reserve, Poda Protected Area and Pomorie Lake Protected Area.</p>
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16 pages, 4037 KiB  
Article
Water and Wastewater Management in Production Processes of PGE Energia Ciepła SA Branch 1 in Krakow in Light of Company Modernization
by Zbigniew Kowalczyk and Wojciech Winiarski
Sustainability 2024, 16(15), 6686; https://doi.org/10.3390/su16156686 - 5 Aug 2024
Viewed by 316
Abstract
Electricity production requires a very high water consumption. One way to reduce water demand in power plants might be effective wastewater recycling within the power plant, which can lead to almost zero wastewater discharge. The study aims to characterize the functioning of the [...] Read more.
Electricity production requires a very high water consumption. One way to reduce water demand in power plants might be effective wastewater recycling within the power plant, which can lead to almost zero wastewater discharge. The study aims to characterize the functioning of the water and wastewater management system before and after the modernization of a wastewater treatment installation owned by an electricity and heat producer using biomass and other solid fuels. The scope of work covered one of the largest energy companies in Poland: PGE Energia Ciepła SA Branch 1 in Krakow. Water management and the effectiveness of wastewater treatment installation modernization were assessed in terms of the BAT (Best Available Techniques) conclusions. Particular attention was paid to the analysis of changes in the quality parameters of wastewater after the modernization of the wet flue gas desulfurization installation. The research results prove that the modernization of the company’s water and wastewater system significantly reduced the emission of harmful substances into the environment and water consumption. After modernization, an effective reduction in the content of heavy metals and other pollutants in the wastewater was observed. A decrease in the content of cadmium was observed by 99%, nickel—96%, mercury—95%, and copper—83%. Full article
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<p>Diagram of the water and wastewater system at PGE Energia Ciepła in Krakow. Source: own elaboration based on [<a href="#B46-sustainability-16-06686" class="html-bibr">46</a>].</p>
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<p>Scheme of the decarbonization system for raw water from the Białucha River. Source: own elaboration based on [<a href="#B47-sustainability-16-06686" class="html-bibr">47</a>,<a href="#B48-sustainability-16-06686" class="html-bibr">48</a>].</p>
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<p>Diagram of the decarbonized water filtration system. Source: own elaboration based on [<a href="#B47-sustainability-16-06686" class="html-bibr">47</a>,<a href="#B48-sustainability-16-06686" class="html-bibr">48</a>].</p>
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<p>Diagram of the water deionization and demineralization system. Source: own elaboration based on [<a href="#B47-sustainability-16-06686" class="html-bibr">47</a>,<a href="#B48-sustainability-16-06686" class="html-bibr">48</a>].</p>
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<p>Scheme of the wastewater treatment installation no. 1. Source: own elaboration based on [<a href="#B47-sustainability-16-06686" class="html-bibr">47</a>,<a href="#B48-sustainability-16-06686" class="html-bibr">48</a>].</p>
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<p>Diagram of the wet flue gas desulfurization treatment installation before modernization. Source: own elaboration based on [<a href="#B46-sustainability-16-06686" class="html-bibr">46</a>].</p>
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<p>Diagram of the wet flue gas desulfurization treatment installation after modernization. Source: own elaboration based on [<a href="#B46-sustainability-16-06686" class="html-bibr">46</a>].</p>
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22 pages, 1649 KiB  
Article
The Contribution of Trichoderma viride and Metallothioneins in Enhancing the Seed Quality of Avena sativa L. in Cd-Contaminated Soil
by Wiktoria Konieczna, Sena Turkan, Marzena Warchoł, Edyta Skrzypek, Grażyna B. Dąbrowska and Agnieszka Mierek-Adamska
Foods 2024, 13(15), 2469; https://doi.org/10.3390/foods13152469 - 5 Aug 2024
Viewed by 485
Abstract
Pollution of arable land with heavy metals is a worldwide problem. Cadmium (Cd) is a toxic metal that poses a severe threat to humans’ and animals’ health and lives. Plants can easily absorb Cd from the soil, and plant-based food is the main [...] Read more.
Pollution of arable land with heavy metals is a worldwide problem. Cadmium (Cd) is a toxic metal that poses a severe threat to humans’ and animals’ health and lives. Plants can easily absorb Cd from the soil, and plant-based food is the main means of exposure to this hazardous element for humans and animals. Phytoremediation is a promising plant-based approach to removing heavy metals from the soil, and plant growth-promoting micro-organisms such as the fungi Trichoderma can enhance the ability of plants to accumulate metals. Inoculation of Avena sativa L. (oat) with Trichoderma viride enhances germination and seedling growth in the presence of Cd and, in this study, the growth of 6-month-old oat plants in Cd-contaminated soil was not increased by inoculation with T. viride, but a 1.7-fold increase in yield was observed. The content of Cd in oat shoots depended on the Cd content in the soil. Still, it was unaffected by the inoculation with T. viride. A. sativa metallothioneins (AsMTs) participate in plant–fungi interaction, however, their role in this study depended on MT type and Cd concentration. The inoculation of A. sativa with T. viride could be a promising approach to obtaining a high yield in Cd-contaminated soil without increasing the Cd content in the plant. Full article
(This article belongs to the Section Plant Foods)
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Graphical abstract

Graphical abstract
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<p>Effect of <span class="html-italic">Trichoderma viride</span> T5 inoculation on the growth of <span class="html-italic">Avena sativa</span> plants in soil containing 1 mg, 5 mg, 10 mg, and 20 mg of Cd per 1 kg of soil. Length, fresh and dry biomass of shoot (A, C, E, respectively) and root (B, D, F, respectively) were measured. Bars represent means (<span class="html-italic">n</span> = 40) ± SE. Means indicated with distinct letters are significantly different (Kruskal–Wallis, Dunn post hoc test, <span class="html-italic">p</span> &lt; 0.05).</p>
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<p>Pearson correlation between the amount of cadmium added to the soil, number of seeds, levels of Cu, Zn, and Cd in <span class="html-italic">Avena sativa</span> shoots, and the inoculation of oat seeds with <span class="html-italic">Trichoderma viride</span> T5 spores. Only significant correlations are shown.</p>
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<p>Comparison of the growth of <span class="html-italic">Escherichia coli</span> cells transformed with empty pET21a(+) vector and pET21a(+) vectors harbouring coding regions of <span class="html-italic">AsMT1-4</span> in LB medium (control) and LB medium supplemented with Zn or Cd ions. The expression of <span class="html-italic">AsMT1-4</span> was induced by 0.1 mM IPTG. The relative growth rate is expressed as a slope of bacterial growth curves obtained by plotting optical density against time. Bars represent means (<span class="html-italic">n</span> = 9) ± SE. The results obtained for a given condition were compared, and distinct letters indicate significant differences between <span class="html-italic">E. coli</span> carrying different plasmids (Kruskal–Wallis, Mann–Whitney; <span class="html-italic">p</span> &lt; 0.05).</p>
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<p>Relative gene expression of <span class="html-italic">Avena sativa</span> metallothioneins (<b>A</b>) <span class="html-italic">A</span>s<span class="html-italic">MT1</span>, (<b>B</b>) <span class="html-italic">A</span>s<span class="html-italic">MT2</span>, (<b>C</b>) <span class="html-italic">A</span>s<span class="html-italic">MT3</span>, and (<b>D</b>) <span class="html-italic">A</span>s<span class="html-italic">MT4</span> in two-week-old oat seedlings, inoculated (green bars) or non-inoculated (blue bars) with <span class="html-italic">Trichoderma viride</span> T5, grown in soil containing 1, 5, 10, and 20 mg Cd per kg of soil. Bars represent means (<span class="html-italic">n</span> = 2) ± SE. Distinct letters mark significant differences (one-way ANOVA, Tukey post hoc test, <span class="html-italic">p</span> &lt; 0.05).</p>
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12 pages, 2365 KiB  
Article
Citrate Dialysate with and without Magnesium Supplementation in Hemodiafiltration: A Comparative Study Versus Acetate
by Diana Rodríguez-Espinosa, Elena Cuadrado-Payán, Naira Rico, Mercè Torra, Rosa María Fernández, Gregori Casals, María Rodríguez-García, Francisco Maduell and José Jesús Broseta
Int. J. Mol. Sci. 2024, 25(15), 8491; https://doi.org/10.3390/ijms25158491 - 3 Aug 2024
Viewed by 370
Abstract
The choice of dialysate buffer in hemodialysis is crucial, with acetate being widely used despite complications. Citrate has emerged as an alternative because of its favorable effects, yet concerns persist about its impact on calcium and magnesium levels. This study investigates the influence [...] Read more.
The choice of dialysate buffer in hemodialysis is crucial, with acetate being widely used despite complications. Citrate has emerged as an alternative because of its favorable effects, yet concerns persist about its impact on calcium and magnesium levels. This study investigates the influence of citrate dialysates (CDs) with and without additional magnesium supplementation on CKD-MBD biomarkers and assesses their ability to chelate divalent metals compared to acetate dialysates (ADs). A prospective crossover study was conducted in a single center, involving patients on thrice-weekly online hemodiafiltration (HDF). The following four dialysates were compared: two acetate-based and two citrate-based. Calcium, magnesium, iPTH, iron, selenium, cadmium, copper, zinc, BUN, albumin, creatinine, bicarbonate, and pH were monitored before and after each dialysis session. Seventy-two HDF sessions were performed on eighteen patients. The CDs showed stability in iPTH levels and reduced post-dialysis total calcium, with no significant increase in adverse events. Magnesium supplementation with CDs prevented hypomagnesemia. However, no significant differences among dialysates were observed in the chelation of other divalent metals. CDs, particularly with higher magnesium concentrations, offer promising benefits, including prevention of hypomagnesemia and stabilization of CKD-MBD parameters, suggesting citrate as a viable alternative to acetate. Further studies are warranted to elucidate long-term outcomes and optimize dialysate formulations. Until then, given our results, we recommend that when a CD is used, it should be used with a 0.75 mmol/L Mg concentration rather than a 0.5 mmol/L one. Full article
(This article belongs to the Special Issue Exploring the Molecular Mechanisms of Chronic Kidney Disease)
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<p>Violin plots of pre- and post-dialysis concentrations with each dialysate for (<b>A</b>). magnesium, (<b>B</b>). ionized calcium, (<b>C</b>). total calcium, (<b>D</b>). PTH, (<b>E</b>). iron, (<b>F</b>). copper, (<b>G</b>). zinc, (<b>H</b>). selenium, and (<b>I</b>). cadmium. iPTH: intact parathyroid hormone. SmartBag<sup>®</sup> 211.25: acetate dialysate with a calcium concentration of 1.25 mmol/L and magnesium concentration of 0.5 mmol/L, SmartBag<sup>®</sup> 211.5: acetate dialysate with a calcium concentration of 1.5 mmol/L and magnesium concentration of 0.5 mmol/L, SmartBag<sup>®</sup> CA 211.5: citrate dialysate with a calcium concentration of 1.5 mmol/L and magnesium concentration of 0.5 mmol/L, and SmartBag<sup>®</sup> CA 211.5-0.75: citrate dialysate with a calcium concentration of 1.5 mmol/L and magnesium concentration of 0.75 mmol/L.</p>
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<p>Correlation of the delta between the pre- and post-dialysis intact PTH blood concentration with iCa (<b>A</b>), total calcium (<b>B</b>), and magnesium (<b>C</b>) blood values. iCa, ionized calcium; iPTH, intact parathyroid hormone.</p>
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26 pages, 2104 KiB  
Article
Effects of Dietary Chitosan on Growth Performance, Serum Biochemical Indices, Antioxidant Capacity, and Immune Response of Juvenile Tilapia (Oreochromis niloticus) under Cadmium Stress
by Qin Zhang, Yi Xie, Jiaqiong Tang, Liuqing Meng, Enhao Huang, Dongsheng Liu, Tong Tong, Yongqiang Liu and Zhongbao Guo
Animals 2024, 14(15), 2259; https://doi.org/10.3390/ani14152259 - 3 Aug 2024
Viewed by 277
Abstract
The objective of this study was to examine the effects of varying levels of dietary chitosan supplementation on mitigating cadmium stress and its influence on growth performance, serum biochemical indices, antioxidant capacity, immune response, inflammatory response, and the expression of related genes in [...] Read more.
The objective of this study was to examine the effects of varying levels of dietary chitosan supplementation on mitigating cadmium stress and its influence on growth performance, serum biochemical indices, antioxidant capacity, immune response, inflammatory response, and the expression of related genes in juvenile Genetically Improved Farmed Tilapia (GIFT, Oreochromis niloticus). Five groups of juvenile tilapias (initial body weight 21.21 ± 0.24 g) were fed five diets with different levels (0%, 0.5%, 1.0%, 1.5%, and 2.0%) of chitosan supplementation for 60 days under cadmium stress (0.2 mg/L Cd2+). The findings indicated that, compared with the 0% chitosan group, dietary chitosan could significantly increase (p < 0.05) the final weight (Wf), weight gain rate (WGR), specific growth rate (SGR), daily growth index (DGI), and condition factor (CF), while the feed conversion ratio (FCR) expressed the opposite trend in juvenile GIFT. Dietary chitosan could significantly increase (p < 0.05) the activities (contents) of cholinesterase (CHE), albumin (ALB), lactate dehydrogenase (LDH), alkaline phosphatase (ALP), acid phosphatase (ACP), and lysozyme (LZM), while glutamic pyruvic transaminase (GPT), glutamic oxaloacetic transaminase (GOT), and complement 3 (C3) in the serum of juvenile GIFT expressed the opposite trend. Dietary chitosan could significantly increase (p < 0.05) the activities of superoxide dismutase (SOD) and catalase (CAT) and significantly decrease (p < 0.05) the activities (contents) of glutathione S-transferase (GST), glutathione peroxidase (GSH-Px), and malondialdehyde (MDA) in the serum of juvenile GIFT. Dietary chitosan could significantly increase (p < 0.05) the activities (contents) of CAT, GST, GSH-Px, and total antioxidant capacity (T-AOC) and significantly decrease (p < 0.05) the contents of MDA in the liver of juvenile GIFT. Dietary chitosan could significantly increase (p < 0.05) the activities (contents) of SOD, GSH-Px, T-AOC, Na+-K+-ATPase, and Ca2+-ATPase and significantly decrease (p < 0.05) the activities (contents) of CAT, GST, and MDA in the gills of juvenile GIFT. Dietary chitosan could significantly up-regulate (p < 0.05) the gene expression of cat, sod, gst, and gsh-px in the liver of juvenile GIFT. Dietary chitosan could significantly up-regulate (p < 0.05) the gene expression of interferon-γ (inf-γ) in the gills and spleen and significantly down-regulate (p < 0.05) the gene expression of inf-γ in the liver and head kidney of juvenile GIFT. Dietary chitosan could significantly down-regulate (p < 0.05) the gene expression of interleukin-6 (il-6), il-8, and tumor necrosis factor-α (tnf-α) in the liver, gills, head kidney, and spleen of juvenile GIFT. Dietary chitosan could significantly up-regulate (p < 0.05) the gene expression of il-10 in the liver, gills, head kidney, and spleen of juvenile GIFT. Dietary chitosan could significantly up-regulate (p < 0.05) the gene expression of transforming growth factor-β (tgf-β) in the liver and significantly down-regulate (p < 0.05) the gene expression of tgf-β in the head kidney and spleen of juvenile GIFT. In conclusion, dietary chitosan could mitigate the impact of cadmium stress on growth performance, serum biochemical indices, antioxidant capacity, immune response, inflammatory response, and related gene expression in juvenile GIFT. According to the analysis of second-order polynomial regression, it was found that the optimal dietary chitosan levels in juvenile GIFT was approximately 1.42% to 1.45%, based on its impact on Wf, WGR, SGR, and DGI. Full article
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<p>Relationship between different dietary chitosan levels and the final weight (Wf), weight gain rate (WGR), specific growth rate (SGR), and daily growth index (DGI) of juvenile GIFT under cadmium stress based on second-order polynomial regression analysis.</p>
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<p>Effects of dietary chitosan on ATPase activity in the gills of juvenile GIFT under cadmium stress. All the above data are mean ± SE (<span class="html-italic">n</span> = 3). Different superscript letters in the figure indicate significant differences among the data (<span class="html-italic">p</span> &lt; 0.05).</p>
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<p>Effects of dietary chitosan on the relative expression of catalase (<span class="html-italic">cat</span>), superoxide dismutase (<span class="html-italic">sod</span>), glutathione S-transferase (<span class="html-italic">gst</span>), and glutathione peroxidase (<span class="html-italic">gsh-px</span>) in the liver of juvenile GIFT under cadmium stress. All the above data are mean ± SE (<span class="html-italic">n</span> = 3). Different superscript letters in the figure indicate significant differences among the data (<span class="html-italic">p</span> &lt; 0.05).</p>
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<p>Effects of dietary chitosan on the relative expression of interferon-γ (<span class="html-italic">inf-γ</span>) in the liver, gills, head kidney, and spleen of juvenile GIFT under cadmium stress. All the above data are mean ± SE (<span class="html-italic">n</span> = 3). Different superscript letters in the figure indicate significant differences among the data (<span class="html-italic">p</span> &lt; 0.05).</p>
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<p>Effects of dietary chitosan on the relative expression of interleukin-6 (<span class="html-italic">il-6</span>) in the liver, gills, head kidney, and spleen of juvenile GIFT under cadmium stress. All the above data are mean ± SE (<span class="html-italic">n</span> = 3). Different superscript letters in the figure indicate significant differences among the data (<span class="html-italic">p</span> &lt; 0.05).</p>
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<p>Effects of dietary chitosan on the relative expression of interleukin-8 (<span class="html-italic">il-8</span>) in the liver, gills, head kidney, and spleen of juvenile GIFT under cadmium stress. All the above data are mean ± SE (<span class="html-italic">n</span> = 3). Different superscript letters in the figure indicate significant differences among the data (<span class="html-italic">p</span> &lt; 0.05).</p>
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<p>Effects of dietary chitosan on the relative expression of interleukin-10 (<span class="html-italic">il-10</span>) in the liver, gills, head kidney, and spleen of juvenile GIFT under cadmium stress. All the above data are mean ± SE (<span class="html-italic">n</span> = 3). Different superscript letters in the figure indicate significant differences among the data (<span class="html-italic">p</span> &lt; 0.05).</p>
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<p>Effects of dietary chitosan on the relative expression of transforming growth factor-β (<span class="html-italic">tgf-β</span>) in the liver, gills, head kidney, and spleen of juvenile GIFT under cadmium stress. All the above data are mean ± SE (<span class="html-italic">n</span> = 3). Different superscript letters in the figure indicate significant differences among the data (<span class="html-italic">p</span> &lt; 0.05).</p>
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<p>Effects of dietary chitosan on the relative expression of tumor necrosis factor-α (<span class="html-italic">tnf-α</span>) in the liver, gills, head kidney, and spleen of juvenile GIFT under cadmium stress. All the above data are mean ± SE (<span class="html-italic">n</span> = 3). Different superscript letters in the figure indicate significant differences among the data (<span class="html-italic">p</span> &lt; 0.05).</p>
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20 pages, 6889 KiB  
Article
Exogenous Application of Amino Acids Alleviates Toxicity in Two Chinese Cabbage Cultivars by Modulating Cadmium Distribution and Reducing Its Translocation
by Longcheng Li, Qing Chen, Shihao Cui, Muhammad Ishfaq, Lin Zhou, Xue Zhou, Yanli Liu, Yutao Peng, Yifa Yu and Wenliang Wu
Int. J. Mol. Sci. 2024, 25(15), 8478; https://doi.org/10.3390/ijms25158478 - 3 Aug 2024
Viewed by 290
Abstract
Plants communicate underground by secreting multiple amino acids (AAs) through their roots, triggering defense mechanisms against cadmium (Cd) stress. However, the specific roles of the individual AAs in Cd translocation and detoxification remain unclear. This study investigated how exogenous AAs influence Cd movement [...] Read more.
Plants communicate underground by secreting multiple amino acids (AAs) through their roots, triggering defense mechanisms against cadmium (Cd) stress. However, the specific roles of the individual AAs in Cd translocation and detoxification remain unclear. This study investigated how exogenous AAs influence Cd movement from the roots to the shoots in Cd-resistant and Cd-sensitive Chinese cabbage cultivars (Jingcui 60 and 16-7 cultivars). The results showed that methionine (Met) and cysteine (Cys) reduced Cd concentrations in the shoots of Jingcui 60 by approximately 44% and 52%, and in 16-7 by approximately 43% and 32%, respectively, compared to plants treated with Cd alone. However, threonine (Thr) and aspartic acid (Asp) did not show similar effects. Subcellular Cd distribution analysis revealed that AA supplementation increased Cd uptake in the roots, with Jingcui 60 preferentially storing more Cd in the cell wall, whereas the 16-7 cultivar exhibited higher Cd concentrations in the organelles. Moreover, Met and Cys promoted the formation of Cd-phosphate in the roots of Jingcui 60 and Cd-oxalate in the 16-7 cultivar, respectively. Further analysis showed that exogenous Cys inhibited Cd transport to the xylem by downregulating the expression of HMA2 in the roots of both cultivars, and HMA4 in the 16-7 cultivar. These findings provide insights into the influence of exogenous AAs on Cd partitioning and detoxification in Chinese cabbage plants. Full article
(This article belongs to the Section Molecular Toxicology)
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Figure 1
<p>Effect of Met, Cys, Thr, and Asp on Chinese cabbage (Jingcui 60 and 16-7) growth (<b>A</b>,<b>B</b>) and root length (<b>C</b>,<b>D</b>).</p>
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<p>Effect of Met, Cys, Thr, and Asp on Chinese cabbage (Jingcui 60 and 16-7) shoot weight (g plant<sup>−1</sup> DW) (<b>A</b>), root weight (g plant<sup>−1</sup> DW) (<b>B</b>), root-to-shoot ratio (<b>C</b>), and soil plant analysis development (SPAD) values (<b>D</b>) under 5 μM Cd stress. Each value represents the mean ± SD (n = 3). Letters a–c indicate significant differences between treatments at <span class="html-italic">p</span> &lt; 0.05. ANOVA with Tukey’s post hoc test used for the parametric analysis. Asterisks indicate significant differences between two groups: * <span class="html-italic">p</span> &lt; 0.05; ** <span class="html-italic">p</span> &lt; 0.01; *** <span class="html-italic">p</span> &lt; 0.001. ns indicates no significant difference.</p>
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<p>Effects of Met, Cys, Thr, and Asp applications on the Cd concentration (<b>A</b>,<b>B</b>) and the root:shoot ratio (<b>C</b>) in two Chinese cabbage cultivars under 5 μM Cd stress. Each value is the mean ± SD (n = 3). Letters a-c indicate significant differences between treatments at <span class="html-italic">p</span> &lt; 0.05. ANOVA with Tukey’s post hoc test was used for the parametric analysis. Asterisks indicate significant differences between two groups: ** <span class="html-italic">p</span> &lt; 0.01; *** <span class="html-italic">p</span> &lt; 0.001. ns indicates no significant difference.</p>
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<p>Effect of Met, Cys, Thr, and Asp applications on the subcellular distribution of Cd in the shoot (<b>A</b>,<b>C</b>,<b>E</b>) and root (<b>B</b>,<b>D</b>,<b>F</b>). “nd” indicates "not detected". Leaf60 refers to the leaf of the Jingcui 60 cultivar, Leaf16 refers to the leaf of the 16-7 cultivar, Root60 refers to the root of the Jingcui 60, and Root16 refers to the root of the 16-7 cultivar. Plant cells were separated into cell wall fraction (Fcw), organelle fraction (Fo), and soluble fraction (Fs), where n = 3. Letters a-c indicate significant differences between treatments at <span class="html-italic">p</span> &lt; 0.05. ANOVA with Tukey’s post hoc test was used for the parametric analysis. Asterisks indicate significant differences between two groups: * <span class="html-italic">p</span> &lt; 0.05; ** <span class="html-italic">p</span> &lt; 0.01; *** <span class="html-italic">p</span> &lt; 0.001. ns indicates no significant difference.</p>
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<p>Concentrations of different chemical forms of Cd in the shoots (<b>A</b>–<b>F</b>) and roots (<b>G</b>–<b>L</b>) of Jingcui 60 and 16-7 cultivars with AA application. Leaf60 refers to the leaf of the Jingcui 60 cultivar, Leaf16 refers to the leaf of the 16-7 cultivar, Root60 refers to the root of the Jingcui 60, and Root16 refers to the root of the 16-7 cultivar. These chemical forms represent the fractions extracted by 80% ethanol (inorganic Cd, F1), deionized water (Cd-organic acid complexes, F2), 1 M NaCl (pectate-integrated Cd, F3), 2% acetic acid (Cd-phosphate, F4), 0.6 M HCl (Cd-oxalate, F5), and the residue (F6). Letters a-c indicate significant differences between treatments at <span class="html-italic">p</span> &lt; 0.05. ANOVA with Tukey’s post hoc test was used for the parametric analysis. Asterisks indicate significant differences between two groups: * <span class="html-italic">p</span> &lt; 0.05; ** <span class="html-italic">p</span> &lt; 0.01; *** <span class="html-italic">p</span> &lt; 0.001. ns indicates no significant difference.</p>
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<p>Proportion of Cd (%) in different subcellular fractions (<b>A</b>) and chemical forms of Cd (<b>B</b>) in the roots of both Chinese cabbage cultivars.</p>
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<p>Principal component analysis (PCA) was used to examine the relationship between the subcellular distribution and chemical forms of Cd in the root, and Cd concentrations in the shoot and root (<b>A</b>,<b>B</b>). The circle and square refer to the samples from the Jingcui 60 and 16-7 cultivars, respectively. The colors (red, green, pink, blue, and black, respectively) represent Cd, Cd + Met, Cd + Cys, Cd + Thr, and Cd + Asp treatments. Abbreviations: shoot Cd, Cd concentration in the shoots; DW, dry weight; Fcw, cell wall fraction; Fo, organelle fraction; Fs, soluble fraction; F1, inorganic Cd extracted by 80% ethanol; F2, Cd-organic acid complexes extracted by DI water; F3, pectate-integrated Cd; F4, insoluble Cd-phosphate; F5, Cd-oxalate; F6, Cd in the residues.</p>
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<p>The expressions of <span class="html-italic">HMA2</span>, <span class="html-italic">HMA4</span>, <span class="html-italic">HMA3</span>, <span class="html-italic">PCS1</span>, <span class="html-italic">ABCC1</span>, <span class="html-italic">ABCC2</span>, <span class="html-italic">IRT1</span>, and <span class="html-italic">IRT2</span> in roots of both cultivars under Cd + Cys and Cd + Thr treatments (<b>A</b>–<b>H</b>). Data are presented as means ± SD, and different letters on the bars indicate significant differences at <span class="html-italic">p</span> &lt; 0.05 (n = 3 plants for each replicate). ANOVA with Tukey’s post hoc test was used for the parametric analysis.</p>
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<p>Different Cd concentrations and toxicity symptoms in Chinese cabbage. (<b>A</b>) Growth stages (5th, 6th, and 7th of full leaf) of Chinese cabbage under control conditions and treated with 5 μM Cd. (<b>B</b>) Shoot weight of Chinese cabbage under the four treatments (CK, 5th, 6th, and 7th). (<b>C</b>) Phenotypes of Chinese cabbage under control conditions and treated with 5, 10, and 20 μM Cd. (<b>D</b>) soil plant analysis development (SPAD) values of Chinese cabbage under the four treatments (CK, 5, 10, and 20 μM) in hydroponic conditions. All phenotypes were observed after four days of treatment. For all parameters, n represents the number of biologically independent samples. Different letters indicate significant differences among groups. ANOVA with Tukey’s post hoc test was used for the parametric analysis. Asterisks indicate significant differences between groups: * <span class="html-italic">p</span> &lt; 0.05; ** <span class="html-italic">p</span> &lt; 0.01; *** <span class="html-italic">p</span> &lt; 0.001. ns indicates no significant difference.</p>
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<p>Phenotypes of Chinese cabbage (Jingcui 60) under control conditions and when treated with sole Cd and Cd + methionine (Met)/cysteine (Cys) at concentrations of 25, 50, 100, and 200 μM (<b>A</b>,<b>B</b>). The Cd concentrations in the shoots (<b>C</b>) and roots (<b>D</b>). All treatments were replicated three times. Different lowercase letters indicate significant differences among treatments. ANOVA with Tukey’s post hoc test was used for the parametric analysis. Asterisks indicate significant differences between groups: * <span class="html-italic">p</span> &lt; 0.05; *** <span class="html-italic">p</span> &lt; 0.001. ns indicates no significant difference.</p>
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<p>Cd concentrations in the shoots (<b>a</b>) and roots (<b>b</b>) of Jingcui 60 cultivars grown under Cd stress (5 μM) and treated with glycine (50 μM, Gly), proline (Pro), threonine (Thr), aspartic acid (Asp), cysteine (Cys), methionine (Met), glutamic acid (Glu), and gamma-aminobutyric acid (GABA). Different lowercase letters indicate significant differences among treatments. One-way ANOVA with Tukey’s post hoc test was used for the parametric analysis.</p>
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<p>Effect of AA treatment on the activity of the antioxidant enzymes. (<b>A</b>) MDA content, (<b>B</b>) H<sub>2</sub>O<sub>2</sub> content, (<b>C</b>) activity of CAT, (<b>D</b>) activity of POD, and (<b>E</b>) activity of SOD in the shoots. All values represent the mean ± standard deviation (SD), <span class="html-italic">n</span> = 3. Different lower letters indicate significant differences among treatments. ANOVA with Tukey’s post hoc test is used for the parametric test. Asterisks indicate significant differences between two groups: * <span class="html-italic">p</span> &lt; 0.05; ** <span class="html-italic">p</span> &lt; 0.01; *** <span class="html-italic">p</span> &lt; 0.001. ns indicates no significant difference.</p>
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<p>Xylem sap volumes (<b>A</b>) and Cd concentrations (<b>B</b>) of xylem sap collected from Jingcui 60 and 16-7 with Cys and Thr treatments. Data are presented as means ± SDs, and different letters on the bars indicate significant differences at α = 0.05 (n = 4 plants for each replicate). ANOVA with Tukey’s post hoc test was used for the parametric analysis. Asterisks indicate significant differences between two groups: *** <span class="html-italic">p</span> &lt; 0.001. ns indicates no significant difference.</p>
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22 pages, 9734 KiB  
Article
Implications of Water Quality Index and Multivariate Statistics for Improved Environmental Regulation in the Irtysh River Basin (Kazakhstan)
by Ultuar Zhalmagambetova, Daulet Assanov, Alexandr Neftissov, Andrii Biloshchytskyi and Ivan Radelyuk
Water 2024, 16(15), 2203; https://doi.org/10.3390/w16152203 - 2 Aug 2024
Viewed by 623
Abstract
The selection of sites for permanent environmental monitoring of natural water bodies should rely on corresponding source apportionment studies. Tools like the water quality index (WQI) assessment may support this objective. This study aims to analyze a decade-long dataset of measurements of 26 [...] Read more.
The selection of sites for permanent environmental monitoring of natural water bodies should rely on corresponding source apportionment studies. Tools like the water quality index (WQI) assessment may support this objective. This study aims to analyze a decade-long dataset of measurements of 26 chemical components at 26 observation points within the Irtysh River Basin, aiming to identify priority zones for stricter environmental regulations. It was achieved through the WQI tool integrated with geoinformation systems (GISs) and multivariate statistical techniques. The findings highlighted that both upstream sections of tributaries (Oba and Bukhtarma rivers) and the mainstream of the basin are generally in good condition, with slight fluctuations observed during flooding periods. Areas in the basin experiencing significant impacts from mining and domestic wastewater treatment activities were identified. The rivers Glubochanka (GL) and Krasnoyarka (KR) consistently experienced marginal water quality throughout the observation period. Various contaminant sources were found to influence water quality. The impact of domestic wastewater treatment facilities was represented by twofold elevated concentrations of chemical oxygen demand, reaching 22.6 and 27.1 mg/L for the KR and GL rivers, respectively. Natural factors were indicated by consistent slight exceedings of recommended calcium levels at the KR and GL rivers. These exceedances were most pronounced during the cold seasons, with an average value equal to 96 mg/L. Mining operations introduced extremal concentrations of trace elements like copper, reaching 0.046–0.051 mg/L, which is higher than the threshold by 12–13 times; zinc, which peaked at 1.57–2.96 mg/L, exceeding the set limit by almost 50–100 times; and cadmium, peaking at levels surpassing 1000 times the safe limit, reaching 0.8 mg/L. The adverse impact of mining activities was evident in the Tikhaya, Ulba, and Breksa rivers, showing similar trends in trace element concentrations. Seasonal effects were also investigated. Ice cover formation during cold seasons led to oxygen depletion and the exclusion of pollutants into the stream when ice melted, worsening water quality. Conversely, flooding events led to contaminant dilution, partially improving the WQI during flood seasons. Principal component analysis and hierarchical cluster analysis indicated that local natural processes, mining activities, and domestic wastewater discharge were the predominant influences on water quality within the study area. These findings can serve as a basis for enhanced environmental regulation in light of updated ecological legislation in Kazakhstan, advocating for the establishment of a comprehensive monitoring network and the reinforcement of requirements governing contaminating activities. Full article
(This article belongs to the Section Water Quality and Contamination)
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<p>Study area.</p>
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<p>Flow rates (m<sup>3</sup>/s) along the main course of the Irtysh River Basin in Kazakhstan. The top graph displays the monthly average flow rates at the stations. Source: [<a href="#B9-water-16-02203" class="html-bibr">9</a>] (Open Access).</p>
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<p>Temporal variation of selected chemicals within the studied period in the observation points with fair and marginal water quality status.</p>
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<p>Average seasonal concentrations of indicative chemicals in the observation points with fair and marginal water quality status.</p>
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<p>Distribution of WQI within the study area during cold seasons.</p>
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<p>Dendrogram illustrating clustering of sampling sites based on water quality characteristics during cold seasons.</p>
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<p>Distribution of WQI within the study area during flooding seasons.</p>
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<p>Dendrogram illustrating clustering of sampling sites based on water quality characteristics during flooding seasons.</p>
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<p>Distribution of WQI within the study area during warm seasons.</p>
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<p>Dendrogram illustrating clustering of sampling sites based on water quality characteristics during warm seasons.</p>
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14 pages, 3283 KiB  
Article
Genome-Wide Identification of Glutathione S-Transferase Family from Dendrobium officinale and the Functional Characterization of DoGST5 in Cadmium Tolerance
by Wu Jiang, Tao Wang, Man Zhang, Xiaojing Duan, Jiadong Chen, Yingying Liu, Zhengming Tao and Qiaosheng Guo
Int. J. Mol. Sci. 2024, 25(15), 8439; https://doi.org/10.3390/ijms25158439 - 2 Aug 2024
Viewed by 241
Abstract
Glutathione S-transferases (GSTs) are members of a protein superfamily with diverse physiological functions, including cellular detoxification and protection against oxidative damage. However, there is limited research on GSTs responding to cadmium (Cd) stress. This study classified 46 GST genes in Dendrobium officinale ( [...] Read more.
Glutathione S-transferases (GSTs) are members of a protein superfamily with diverse physiological functions, including cellular detoxification and protection against oxidative damage. However, there is limited research on GSTs responding to cadmium (Cd) stress. This study classified 46 GST genes in Dendrobium officinale (D. officinale) into nine groups using model construction and domain annotation. Evolutionary analysis revealed nine subfamilies with diverse physical and chemical properties. Prediction of subcellular localization revealed that half of the GST members were located in the cytoplasm. According to the expression analysis of GST family genes responding to Cd stress, DoGST5 responded significantly to Cd stress. Transient expression of DoGST5-GFP in tobacco leaves revealed that DoGST5 was localized in the cytoplasm. DoGST5 overexpression in Arabidopsis enhanced Cd tolerance by reducing Cd-induced H2O2 and O2 levels. These findings demonstrate that DoGST5 plays a critical role in enhancing Cd tolerance by balancing reactive oxygen species (ROS) levels, offering potential applications for improving plant adaptability to heavy metal stress. Full article
(This article belongs to the Special Issue Advanced Plant Molecular Responses to Abiotic Stresses)
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<p>Phylogenetic tree of DoGSTs (contains GST family proteins of <span class="html-italic">Dendrobium officinale</span>, rice, and Arabidopsis).</p>
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<p>Gene structures and conserved motifs of DoGSTs. (<b>A</b>) Exon-intron organization of DoGST genes. Exons are shown as red rectangles; introns are shown as gray lines. (<b>B</b>) Composition and distributions of conserved motifs in DoGST proteins. The conserved motifs are represented by different numbers and rectangle colors.</p>
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<p>Prediction of TF binding sites on the promoter of GST family genes in <span class="html-italic">Dendrobium officinale.</span> The 2 kb upstream of the translation site was obtained for analysis, and the different colors represent the different of cis-acting elements in the promoter region of each <span class="html-italic">DoGST</span> gene.</p>
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<p>Expression analysis of GST family genes in response to Cd stress in <span class="html-italic">Dendrobium officinale</span>. T01 represents 0 mg·L<sup>−1</sup> Cd treatment as the control. T10, T11, and T12 represent three biological repeats of 14 mg·L<sup>−1</sup> Cd treatment for 15 days. T13, T14, and T15 represent three biological repeats of 14 mg·L<sup>−1</sup> Cd treatment for 30 days.</p>
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<p>Subcellular localization of DoGST5 in <span class="html-italic">N. benthamiana</span> epidermal cells. Upper panel: 35S:GFP plasmid was transformed into <span class="html-italic">N. benthamiana</span> leaves. Lower panel: the fusion protein DoGST5::sGFP was transiently co-expressed with the RFP-rk plasma membrane marker into <span class="html-italic">N. benthamiana</span> leaves, bar = 20 μm.</p>
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<p>Overexpression of <span class="html-italic">DoGST5</span> enhances Cd tolerance in Arabidopsis by reducing the excessive accumulation of ROS induced by Cd stress. (<b>A</b>,<b>B</b>) Phenotypic analysis of Cd tolerance in Arabidopsis overexpressing <span class="html-italic">DoGST5</span>. Col-0 and <span class="html-italic">DoGST5</span> overexpression Arabidopsis lines were cultured on 0 and 60 μM 1/2 MS solid medium for 14 days. (<b>C</b>,<b>D</b>) Primary root length and fresh weight of Col-0 and <span class="html-italic">DoGST5</span> overexpression lines. Data are means ± SD (<span class="html-italic">n</span> = 5). (<b>E</b>,<b>F</b>) Overexpression of <span class="html-italic">DoGST5</span> in Arabidopsis reduces excessive ROS levels induced by Cd stress. Columns with different letters indicate significant differences (<span class="html-italic">p</span>  &lt;  0.05) using one-way ANOVA with Tukey’s test for multiple comparisons.</p>
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21 pages, 3103 KiB  
Article
Heavy Metal Concentrations in Wild Mussels Mytilus galloprovincialis (Lamarck, 1819) during 2001–2023 and Potential Risks for Consumers: A Study on the Romanian Black Sea Coast
by Andra Oros, Elena-Daniela Pantea and Elena Ristea
Sci 2024, 6(3), 45; https://doi.org/10.3390/sci6030045 - 2 Aug 2024
Viewed by 710
Abstract
This study investigates the potential health risks associated with consuming mussels (Mytilus galloprovincialis Lamarck, 1819) from the Romanian Black Sea coast between 2001 and 2023. The research focuses on heavy metal (copper, cadmium, lead, nickel, and chromium) bioaccumulation in mussels and the [...] Read more.
This study investigates the potential health risks associated with consuming mussels (Mytilus galloprovincialis Lamarck, 1819) from the Romanian Black Sea coast between 2001 and 2023. The research focuses on heavy metal (copper, cadmium, lead, nickel, and chromium) bioaccumulation in mussels and the associated human health hazards. While most metals fell within safe limits, lead and cadmium exceeded the maximum admissible concentrations set by the European Commission in a small percentage of samples (10% for cadmium, 14% for lead). To assess human health risks, we calculated dietary intake estimates and hazard quotients. These calculations suggested that current metal concentrations in the mussels are unlikely to cause adverse health effects at typical consumption levels. Although current metal concentrations seem safe based on estimated intake and hazard quotients, we emphasize the need for continuous monitoring of pollutants in seafood to ensure consumer safety. Future research should consider the cumulative effects of various contaminants and how individual factors like age and health conditions might influence risk. Public health protection requires continuous monitoring, comprehensive risk assessments, and transparent communication between scientists, policymakers, and the public to establish safe consumption guidelines. Full article
(This article belongs to the Special Issue Feature Papers—Multidisciplinary Sciences 2024)
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<p>National monitoring network of the Romanian marine waters.</p>
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<p>Biological dredge used for sampling mollusks during monitoring cruises with R/V Steaua de Mare 1 for hazardous substances assessment (NIMRD photo).</p>
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<p>Histograms of heavy metals concentrations in mussels (<span class="html-italic">Mytilus galloprovincialis</span>) investigated during 2001–2023.</p>
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<p>Heavy metals bioaccumulation levels in <span class="html-italic">Mytilus galloprovincialis</span> investigated during 2001–2023 along the Romanian Black Sea coast, bathymetric strip 5–70 m.</p>
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<p>Variability of annual mean values of heavy metals concentrations in <span class="html-italic">Mytilus galloprovincialis</span> from the Romanian Black Sea Sector during 2001–2023.</p>
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<p>Heavy metals (Cd, Pb) values measured in mussels investigated during 2001–2023, compared to the values permitted by European Commission Regulation (EU) 2023/915 for consumed seafood.</p>
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<p>Temporal trend of estimated total hazard quotient (TTHQ) (Cu, Cd, Ni, Cr) for children and adults between 2001 and 2023.</p>
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<p>Temporal trend of averages annual values of total HMs (Cu, Cd, Pb, Ni, Cr) concentrations in mussels and of annual food ingestion rates (FIR) between 2001 and 2023.</p>
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