In this study, hydroponic experiments were conducted to investigate the role of Fe-Mn plaque and Arthrobacter echigonensis MN1405 under different solution Cd levels (0, 2 and 50 mg L) on Cd uptake and translocation by Phytolacca acinosa Roxb. (P. acinosa). Results showed Cd accumulated by P.acinosa without plaque were mostly distributed in root surface, indicating that an exclusion strategy for Cd tolerance. The formation of Fe-Mn plaque could contribute to the increase in the Cd tolerance of P.acinosa, promotion of the growth, increase in the enhancement of Cd translocation. Among all the treatments, Fe-Mn plaque treatments inoculated with MN1405 accumulated the maximum DCB-Cd (46.61 ± 6.36 g kg) and had the highest value of TF (2.14 ± 0.01) at 50 mg L and 2 mg L solution for Cd, respectively, demonstrating the greatest capacity to accumulate and translocate Cd. The uptake of Cd by P. acinosa in plaque treatments may result in the increase of soluble sugar and decrease of soluble protein synthesized from roots which involved in Cd detoxification and thus diminished the negative effects of Cd to some extent.
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http://dx.doi.org/10.1016/j.chemosphere.2017.02.012 | DOI Listing |
Int J Phytoremediation
January 2025
School of Metallurgy and Environment, Central South University, Changsha, China.
The synergistic application of calcium (Ca) and magnesium (Mg) was investigated to mitigate cadmium (Cd) uptake and translocation in rice grown in Cd-contaminated soil. A pot experiment was conducted using different Ca:Mg molar ratios (Ca1:Mg2, Ca2:Mg1, and Ca1:Mg1) to evaluate their effect on Cd uptake. The results showed that the Ca1:Mg1 treatment achieved the highest reduction in grain Cd content (54.
View Article and Find Full Text PDFSci Rep
December 2024
College of Resources and Environment, Department of Environment Science and Engineering, Southwest University, Chongqing, 400715, China.
A pot experiment was conducted on arsenic (As) and cadmium (Cd) co-contaminated soil to discern the influence of varying proportions of pig manure compost (PM) vis-à-vis chemical fertilizers (NPK) on the mitigation of Cd and As absorption by rice. Our findings illustrated that by increasing the PM proportions from 25 to 100%, it manifested a statistically significant reduction in the mobilized fractions of Cd, accounting for up to 77% reduction in soil CaCl-Cd concentrations. Conversely, the NaHCO-As reactions were contingent on the distinct PM application rates.
View Article and Find Full Text PDFJ Environ Manage
November 2024
Institute of Resources, Ecosystem and Environment of Agriculture, Nanjing Agricultural University, 1 Weigang, Nanjing, 210095, China; Jiangsu Collaborative Innovation Center for Solid Organic Waste Resource Utilization, China.
Iron (Fe) modified biochar has been widely used for cadmium (Cd) contaminated soil remediation. However, the accompanying anions introduced during the modification process potentially affect the behavior of Cd in soil. In this study, we investigated the distinct Cd immobilization mechanisms by Fe(SO) modified biochar (FSBC) and Fe(NO) modified biochar (FNBC) in a two-year pot experiment.
View Article and Find Full Text PDFEcotoxicol Environ Saf
March 2024
School of Geographical Sciences, Hunan Normal University, Changsha 410081, China.
Liming has been widely taken to remediate Cd-contaminated acidic paddy soils, whereas liming mode involving in the relevant optimal soil pH, model and efficacies remain unclear. Both soil and field liming experiments were conducted to improve liming mode for precise remediation of Cd-contaminated acidic paddy soils. Soil batch liming experiments indicated soil DTPA-Cd and CaCl-Cd were piecewise linearly correlated to soil pH with nodes of 6.
View Article and Find Full Text PDFSci Total Environ
February 2024
Key Laboratory of Karst Geological Resources and Environment, Ministry of Education, College of Resource and Environmental Engineering, Guizhou University, Guiyang, China.
Biochar (BC) has shown great potential in remediating heavy metal(loid)s (HMs) contamination in paddy fields. Variation in feedstock sources, pyrolysis temperatures, modification methods, and application rates of BC can result in great changes in its effects on HM bioavailability and bioaccumulation in soil-rice systems and remediation mechanisms. Meanwhile, there is a lack of application guidelines for BC with specific properties and application rates when targeting rice fields contaminated with certain HMs.
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