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The DOI matches its Crossref record; 82 of the 82 references it cites were found in a registry or an index; none of the 29 sources its claims cite is checked for support yet.

Integrative biochar and melatonin application mitigates lead toxicity in rice by modulating antioxidant activities and iron plaque formation and downregulating the expression of metal uptake genes

Open access

Abstract

Lead (Pb) is a common toxic metal that causes severe health and environmental problems. However, the defensive role and underlying mechanism of combined biochar (BC) and melatonin (MT) against Pb stress are still unclear. Therefore, to fill this gap, this study investigated the impacts of BC and MT on rice growing in Pb-polluted soil. This study included different treatments: control, Pb stress (300 mg kg−1), Pb stress (300 mg kg−1) + BC (2%), Pb stress (300 mg kg−1) + MT (30 µM), and Pb stress (300 mg kg−1) + BC (2%) + MT (30 µM). Pb reduced rice growth and yield by hindering photosynthetic pigments, relative water contents (RWCs), osmolyte synthesis, nutrient uptake, increase in oxidative markers, and Pb accumulation. Biochar and MT increased rice productivity by increasing chlorophyll synthesis, osmolytes, and nutrient uptake and decreasing Pb accumulation. The co-application of BC and MT decreased Pb accumulation in the roots (30.40%) and shoots (72.79%), the translocation factor (30.01%), the biological accumulation coefficient (20.17%), and the soil Pb concentration (59.02%). The co-application of BC and MT enhanced proline (39.65%), soluble protein (47.09%), ascorbate peroxidase (APX; 26.47%), catalase (CAT; 65.51%), peroxidase (POD; 89.56%), and superoxide dismutase (SOD; 65.53%) activities, which ensured better productivity. Additionally, the BC+MT application increased the expression of antioxidant defense genes (OsAPX, OsCAT, OsPOX, and OsSOD) and decreased the expression of metal transporter genes (OsHMA9 and OsNRAMP5), which protected the rice plants from damage caused by Pb toxicity. These results suggested that BC+MT could be a promising strategy to mitigate Pb toxicity and maintain sustainable and safer food production.

Overview

CoChat Summary

TL;DR

In a pot experiment with Pb-polluted soil, combined biochar (BC) and melatonin (MT) mitigated Pb toxicity in rice more effectively than either alone. The combined treatment reduced Pb accumulation and soil Pb while improving growth, yield, antioxidant defense, osmolyte levels, iron plaque formation, and expression of metal transporter genes.

Key findings

  • Pb stress (300 mg kg−1) reduced rice growth and yield; co-application of BC (2%) + MT (30 µM) decreased root Pb by 30.40%, shoot Pb by 72.79%, translocation factor by 30.01%, biological accumulation coefficient by 20.17%, and soil Pb concentration by 59.02%.
  • BC+MT increased proline by 39.65%, soluble protein by 47.09%, APX by 26.47%, CAT by 65.51%, POD by 89.56%, and SOD by 65.53%, and increased grain yield, biological yield, and harvest index by 54.39%, 33.30%, and 14.65%, respectively.
  • BC+MT increased Fe concentration in root ACA extracts by 67.70% and decreased Pb concentration in ACA extracts by 50.14%; it also upregulated antioxidant genes OsAPX, OsCAT, OsPOX, and OsSOD and downregulated metal transporter genes OsHMA9 and OsNRAMP5 by 96.19% and 83%, respectively, compared with control.

Methods

  • Open-greenhouse pot study at Jiangxi Agricultural University in 2024 using silty loam soil (pH 5.45); treatments were control, Pb stress (300 mg kg−1), Pb+BC (2%), Pb+MT (30 µM), and Pb+BC+MT, arranged in a completely randomized design with three replications.
  • Rice straw biochar was pyrolyzed at 600°C for 8 hours; Pb was applied as PbCl2 and stabilized for 1 month; five 25-day-old rice seedlings were transplanted per pot, and MT was foliar-sprayed 20 days after transplanting.
  • Measured traits included photosynthetic pigments, RWC, oxidative markers, osmolytes, antioxidant enzyme activities, nutrient and Pb concentrations in plant/soil, Pb fractions, iron plaque formation via ACA extraction, and gene expression by qRT-PCR; data were analyzed with one-way ANOVA and Tukey’s HSD, plus PCA and correlation analysis.

Limitations

  • The paper states that more transcriptome and metabolomics studies are needed to validate the results, field studies in contaminated areas are needed before recommendation, and future work should test BC alone and MT alone in unpolluted soils.
  • Evident from the text: findings come from a single greenhouse pot experiment with n = 3, one Pb concentration (300 mg kg−1), one soil type, and one rice cultivar/context, so field-scale and long-term effects are not established.

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Integrity signals

Registry

Crossref · 10.3389/fpls.2025.1609825

Cites

82 of 82 references verified0 citation errors · 0 not checkable

Statistics

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Figures

Figure 1 Scanning electron microscopy analysis of biochar used in the study.
Figure 1 Scanning electron microscopy analysis of biochar used in the study.CC BY · PubMed Central
Figure 2 Effects of biochar and melatonin on root (A), shoot (B), and soil Pb (C) concentration of rice in Pb-polluted soil. The data are mean (n = 3) with ± SD, and different letters with means indicate the significance at p ≤ 0.05.
Figure 2 Effects of biochar and melatonin on root (A), shoot (B), and soil Pb (C) concentration of rice in Pb-polluted soil. The data are mean (n = 3) with ± SD, and different letters with means indicate the significance at p ≤ 0.05.CC BY · PubMed Central
Figure 3 Effects of biochar and melatonin on translocation factor (A) and biological accumulation coefficient of Pb (B). The data are mean (n = 3) with ± SD, and different letters with means indicate the significance at p ≤ 0.05.
Figure 3 Effects of biochar and melatonin on translocation factor (A) and biological accumulation coefficient of Pb (B). The data are mean (n = 3) with ± SD, and different letters with means indicate the significance at p ≤ 0.05.CC BY · PubMed Central
Figure 4 Effects of biochar and melatonin on soil pH (A), AP (B), AK (C), TN (D), and SOC (E). The data are mean (n = 3) with ± SD, and different letters with means indicate the significance at p ≤ 0.05. AP, available phosphorus; AK, available potassium; TN, total nitrogen; SOC, soil organic carbon.
Figure 4 Effects of biochar and melatonin on soil pH (A), AP (B), AK (C), TN (D), and SOC (E). The data are mean (n = 3) with ± SD, and different letters with means indicate the significance at p ≤ 0.05. AP, available phosphorus; AK, available potassium; TN, total nitrogen; SOC, soil organic carbon.CC BY · PubMed Central
Figure 5 Effects of biochar and melatonin application on different fractions of Pb. The data are mean of three replications.
Figure 5 Effects of biochar and melatonin application on different fractions of Pb. The data are mean of three replications.CC BY · PubMed Central
Figure 6 Effects of biochar and melatonin on concentrations of lead (A) and iron (B) in ACA extract of rice roots. The data are mean (n = 3) with ± SD, and different letters with means indicate the significance at p ≤ 0.05. ACA, ascorbic citrate acetic.
Figure 6 Effects of biochar and melatonin on concentrations of lead (A) and iron (B) in ACA extract of rice roots. The data are mean (n = 3) with ± SD, and different letters with means indicate the significance at p ≤ 0.05. ACA, ascorbic citrate acetic.CC BY · PubMed Central
Figure 7 Effects of biochar and melatonin on expression level of antioxidant genes (A–D) and metal transporter genes (E, F) of rice grown under Pb stress. The data are mean (n = 3) with ± SD, and different letters with means indicate the significance at p ≤ 0.05.
Figure 7 Effects of biochar and melatonin on expression level of antioxidant genes (A–D) and metal transporter genes (E, F) of rice grown under Pb stress. The data are mean (n = 3) with ± SD, and different letters with means indicate the significance at p ≤ 0.05.CC BY · PubMed Central
Figure 8 Principal component analysis indicating the impacts of different treatments on collected traits.
Figure 8 Principal component analysis indicating the impacts of different treatments on collected traits.CC BY · PubMed Central
Figure 9 Pearson’s correlation analysis of growth (a), physiological parameters (b), root and shoot Pb and nutrient concentration (c), and soil properties (d). RL, root length; RFW, root fresh weight; RDW, root dry weight; PH, plant height; TPP, tillers/plant; KW, kernel weight; BY, biological yield; GY, grain yield; HI, harvest index; Chl, chlorophyll; Cart, carotenoids; RWC, relative water content; H2O2, hydrogen peroxide; MDA, malondialdehyde; APX, ascorbate peroxidase; CAT, catalase; POD, peroxidase; SOD, superoxide dismutase; pro, proline; TSP, total soluble proteins; N, nitrogen; P, phosphorous; K, potassium; Mg, magnesium; Ca, calcium; AP, available phosphorus; AK, available potassium; TN, total nitrogen; E-Pb, extractable Pb; R-Pb, reducible Pb; O-Pb, oxidizable Pb; Re-Pb, residual Pb.
Figure 9 Pearson’s correlation analysis of growth (a), physiological parameters (b), root and shoot Pb and nutrient concentration (c), and soil properties (d). RL, root length; RFW, root fresh weight; RDW, root dry weight; PH, plant height; TPP, tillers/plant; KW, kernel weight; BY, biological yield; GY, grain yield; HI, harvest index; Chl, chlorophyll; Cart, carotenoids; RWC, relative water content; H2O2, hydrogen peroxide; MDA, malondialdehyde; APX, ascorbate peroxidase; CAT, catalase; POD, peroxidase; SOD, superoxide dismutase; pro, proline; TSP, total soluble proteins; N, nitrogen; P, phosphorous; K, potassium; Mg, magnesium; Ca, calcium; AP, available phosphorus; AK, available potassium; TN, total nitrogen; E-Pb, extractable Pb; R-Pb, reducible Pb; O-Pb, oxidizable Pb; Re-Pb, residual Pb.CC BY · PubMed Central

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Research works printed but not linked: 7

  1. Åkesson, 2015, Joint FAO/WHO food standards programme codex committee on contaminants in foods
  2. Asada, 1987, Production and scavenging of active oxygen in chloroplasts, 227
  3. Bao, 2000, Soil agricultural chemical analysis, 265
  4. Chen, 2022, Assessing simultaneous immobilization of lead and improvement of phosphorus availability through application of phosphorus-rich biochar in a contaminated soil: a pot experiment, Chemosphere, 296, 133891, 10.1016/j.chemosphere.2022.133891 · DOI
  5. 2015, 1006 of 25 June 2015 amending Regulation (EC) No 1881/2006 as regards maximum levels of inorganic arsenic in foodstuffs, Official Journal of the European Union.
  6. Olsen, 1982, Methods of soil analysis: Part 2 chemical and microbiological properties of phosphorus, 403
  7. Zhang, 1992, The measurement and mechanism of lipid peroxidation and SOD, POD and CAT activities in biological system, Res. Method. Crop Physiol., 208

Metadata

Authors
Khan, T. A., Su, Q., Guoqin, H., Du, Z., Noor, M. A., Asseri, T. A. Y., & Hassan, M. U.
Affiliations
  • Jiangxi Agricultural University (CN)
  • Jinggangshan University (CN)
  • King Khalid University (SA)
Corresponding author
  • Su, Qitao
  • Guoqin, Huang
Venue
Frontiers in Plant Science
Published
2025-07-03
Volume
16
Pages
1609825-1609825
ISSN
1664-462X (ISSN-L)
OpenAlex
W4411947837
Cited by
9
References
82
Citations by year
2026: 7 · 2025: 2
FWCI
1.84
Type
journal article
Language
en
Open access
Locations
  • Frontiers in Plant Science (publishedVersion, cc-by)
  • PubMed (publishedVersion)
  • PubMed Central (publishedVersion, cc-by)
  • DOAJ (DOAJ: Directory of Open Access Journals) (submittedVersion, cc-by-sa)
Funders
  • National Natural Science Foundation of China (41661070)
  • King Khalid University
Topics
  • Physical Sciences › Environmental Science › Pollution › Heavy metals in environment
  • Life Sciences › Agricultural and Biological Sciences › Plant Science › Plant Stress Responses and Tolerance
  • Life Sciences › Agricultural and Biological Sciences › Plant Science › Plant Micronutrient Interactions and Effects
Keywords
lead toxicity, biochar, melatonin, rice, heavy metal stress, antioxidant enzymes, OsNRAMP5, proline accumulation, photosynthetic pigments, translocation factor, metal accumulation, soil remediation

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CoChat. (2026). Citation check: Integrative biochar and melatonin application mitigates lead toxicity in rice by modulating antioxidant activities and iron plaque formation and downregulating the expression of metal uptake genes. https://app.cochat.ai/papers/10.3389/fpls.2025.1609825
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Khan, T. A., Su, Q., Guoqin, H., Du, Z., Noor, M. A., Asseri, T. A. Y., & Hassan, M. U. (2025). Integrative biochar and melatonin application mitigates lead toxicity in rice by modulating antioxidant activities and iron plaque formation and downregulating the expression of metal uptake genes. Frontiers in Plant Science. https://doi.org/10.3389/fpls.2025.1609825

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