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The DOI matches its Crossref record; 67 of the 67 references it cites were found in a registry or an index; none of the 41 sources its claims cite is checked for support yet.

Enhanced Lead Phytoextraction by Endophytes from Indigenous Plants

Open access

Abstract

Lead (Pb) is one of the most common metal pollutants in soil, and phytoextraction is a sustainable and cost-effective way to remove it. The purpose of this work was to develop a phytoextraction strategy able to efficiently remove Pb from the soil of a decommissioned fuel depot located in Italy by the combined use of EDTA and endophytic bacteria isolated from indigenous plants. A total of 12 endophytic strains from three native species (Lotus cornicolatus, Sonchus tenerrimus, Bromus sterilis) were isolated and selected to prepare a microbial consortium used to inoculate microcosms of Brassica juncea and Helianthus annuus. As for B. juncea, experimental data showed that treatment with microbial inoculum alone was the most effective in improving Pb phytoextraction in shoots (up to 25 times more than the control). In H. annuus, on the other hand, the most effective treatment was the combined treatment (EDTA and inoculum) with up to three times more Pb uptake values. These results, also validated by the metagenomic analysis, confirm that plant-microbe interaction is a crucial key point in phytoremediation.

Overview

CoChat Summary

TL;DR

This study isolated 12 endophytic strains from native plants at a Pb-contaminated Italian site and tested them, alone or with EDTA, in microcosms of *Brassica juncea* and *Helianthus annuus*. PGPR alone gave the greatest shoot Pb increase in *B. juncea*, while PGPR+EDTA was best in *H. annuus*, with NGS supporting plant-microbe interactions as key.

Key findings

  • A consortium (SG_1) of 12 endophytic strains from *Lotus cornicolatus*, *Sonchus tenerrimus*, and *Bromus sterilis*, selected for at least three plant-growth-promoting traits, was used as inoculum.
  • In *B. juncea*, PGPR alone was most effective for shoot Pb phytoextraction: shoots had approximately 24 times more Pb than control (4.82 vs. 0.20 mg kg⁻¹ in Table 3; abstract reports “up to 25 times”). PGPR+EDTA increased *B. juncea* root Pb accumulation by about 58 times compared with control, and shoot biomass increased 36.5% only in the combined treatment.
  • In *H. annuus*, the combined PGPR+EDTA treatment gave the highest root and shoot Pb concentrations; the abstract reports up to three times more Pb uptake, with shoot values of 3.46 vs. 1.34 mg kg⁻¹ and root values of 42.0 vs. 2.14 mg kg⁻¹. Aerial biomass increased by 13.4% (PGPR alone) and 11.5% (PGPR+EDTA) compared with control.
  • NGS showed communities dominated by Pseudomonadaceae (max 51%), Caulobacteraceae (max 30%), Xanthomonadaceae (max 18%), and Sphingomonadaceae (max 15%); Bacillaceae increased with inoculum from 2% in controls to 8% in PGPR *B. juncea* soil and 5–10% in PGPR *B. juncea* and EDTA+PGPR *H. annuus* soil, while Enterobacteraceae increased with EDTA in roots (0% to 4% for *B. juncea*; 14% to 27% for *H. annuus*).

Methods

  • Soil was collected from six sampling points (SP1–SP6) at a 40,000 m² contaminated site in Italy and mixed into a composite Pb-soil. Microcosms contained 300 g Pb-soil sown with *B. juncea* var. Scala or *H. annuus* var. Paola and received control, PGPR (10⁸ CFU/g soil), or PGPR+EDTA 2 mM, with three replicates over about 30 days.
  • Pb in soil, extracts, and plant tissues was quantified by ICP-OES; soil Pb bioavailability was assessed by sequential extraction with H₂O, KNO₃ 1 M, and EDTA 1%; biomass was recorded as dry weight; phytotoxicity was screened with *Lepidium sativum*; treatment effects used one-way ANOVA with Tukey’s test (p < 0.05).
  • Endophytes were isolated from surface-sterilized roots of the three native species, characterized for PGP traits (IAA, siderophores, P solubilization, EPS, proteolytic activity, ammonia, biofilm, N fixation), and soil/root communities were analyzed by 16S Ion Torrent NGS.

Limitations

  • The paper states that case studies showing positive PGPR-only assisted phytoextraction are limited and that new experiments with different plant species and endophytes are underway; no other limitations are explicitly stated.
  • Evident from the text: the experiment is a short-term (about 30-day) pot microcosm study with three replicates and a single composite soil, so field-scale and longer-term performance are not demonstrated.
  • Evident from the text: Pb contamination levels are inconsistently reported—earlier site values reached approximately 2200 mg kg⁻¹ and exceeded the 1000 mg kg⁻¹ industrial threshold, while the experimental Pb-soil total Pb was about 112 mg kg⁻¹; additionally, NGS sample 2R was excluded due to low data quality.

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Integrity signals

Registry

Crossref · 10.3390/soilsystems5030055

Cites

67 of 67 references verified0 citation errors · 0 not checkable

Statistics

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Figures

Figure 2 ( A ) Root and ( B ) shoot dry weight (mg pot -1 ) of B. juncea and H. annuus grown on Pb-soil control (CT) and Pbsoil treated with, PGPR, and PGPR + EDTA. The values are the mean of three replicates, and the error bars show ± standard deviation. Values with different letters are significantly different at the 5% probability level (Tukey's test). Figure 2. ( A ) Root and ( B ) shoot dry weight (mg pot -1 ) of B. juncea and H. annuus grown on Pb-soil control (CT) and Pb-soil treated with, PGPR, and PGPR + EDTA. The values are the mean of three replicates, and the error bars show ± standard deviation. Values with different letters are significantly different at the 5% probability level (Tukey's test).
Figure 2 ( A ) Root and ( B ) shoot dry weight (mg pot -1 ) of B. juncea and H. annuus grown on Pb-soil control (CT) and Pbsoil treated with, PGPR, and PGPR + EDTA. The values are the mean of three replicates, and the error bars show ± standard deviation. Values with different letters are significantly different at the 5% probability level (Tukey's test). Figure 2. ( A ) Root and ( B ) shoot dry weight (mg pot -1 ) of B. juncea and H. annuus grown on Pb-soil control (CT) and Pb-soil treated with, PGPR, and PGPR + EDTA. The values are the mean of three replicates, and the error bars show ± standard deviation. Values with different letters are significantly different at the 5% probability level (Tukey's test).CC-BY · From the PDF
Figure 3 Effect of PGPR and PGPR + EDTA treatment on Pb uptake by ( A ) root and ( B ) shoot of B. juncea and H. annuus grown on Pb-soil. The values are the mean of three replicates, and the error bars show ± standard deviation. Values with different letters are significantly different at the 5% probability level (Tukey's test). Figure 3. Effect of PGPR and PGPR + EDTA treatment on Pb uptake by ( A ) root and ( B ) shoot of B. juncea and H. annuus grown on Pb-soil. The values are the mean of three replicates, and the error bars show ± standard deviation. Values with different letters are significantly different at the 5% probability level (Tukey's test).
Figure 3 Effect of PGPR and PGPR + EDTA treatment on Pb uptake by ( A ) root and ( B ) shoot of B. juncea and H. annuus grown on Pb-soil. The values are the mean of three replicates, and the error bars show ± standard deviation. Values with different letters are significantly different at the 5% probability level (Tukey's test). Figure 3. Effect of PGPR and PGPR + EDTA treatment on Pb uptake by ( A ) root and ( B ) shoot of B. juncea and H. annuus grown on Pb-soil. The values are the mean of three replicates, and the error bars show ± standard deviation. Values with different letters are significantly different at the 5% probability level (Tukey's test).CC-BY · From the PDF
Figure 4 NGS Ion Torrent analysis of all the samples divided by the B. juncea (i.e., samples 1-3) and H. annuus (i.e., samples 5-8). The numbers represent the different treatments applied (i.e., Controls: 1 and 4; PGPR: 2 and 5; EDTA + PGPR: 3 and 6), and S stands for Soils and R for Roots. Sample 2 R was not included due to the low quality of the data required. Due to the high number of results obtained, the calculations, at the family level, were carried on by setting a cut-off < 2%. Figure 4. NGS Ion Torrent analysis of all the samples divided by the B. juncea (i.e., samples 1-3) and H. annuus (i.e., samples 5-8). The numbers represent the different treatments applied (i.e., Controls: 1 and 4; PGPR: 2 and 5; EDTA + PGPR: 3 and 6), and S stands for Soils and R for Roots. Sample 2 R was not included due to the low quality of the data required. Due to the high number of results obtained, the calculations, at the family level, were carried on by setting a cut-off < 2%.
Figure 4 NGS Ion Torrent analysis of all the samples divided by the B. juncea (i.e., samples 1-3) and H. annuus (i.e., samples 5-8). The numbers represent the different treatments applied (i.e., Controls: 1 and 4; PGPR: 2 and 5; EDTA + PGPR: 3 and 6), and S stands for Soils and R for Roots. Sample 2 R was not included due to the low quality of the data required. Due to the high number of results obtained, the calculations, at the family level, were carried on by setting a cut-off < 2%. Figure 4. NGS Ion Torrent analysis of all the samples divided by the B. juncea (i.e., samples 1-3) and H. annuus (i.e., samples 5-8). The numbers represent the different treatments applied (i.e., Controls: 1 and 4; PGPR: 2 and 5; EDTA + PGPR: 3 and 6), and S stands for Soils and R for Roots. Sample 2 R was not included due to the low quality of the data required. Due to the high number of results obtained, the calculations, at the family level, were carried on by setting a cut-off < 2%.CC-BY · From the PDF

Verification

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Citations

Cites

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  1. (2006). Legislative Decree 152/2006. Rules in environmental field. Italian Official Journal, National Legislation.

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Metadata

Authors
Pietrini, I., Grifoni, M., Franchi, E., Cardaci, A., Pedron, F., Barbafieri, M., Petruzzelli, G., & Vocciante, M.
Affiliations
  • Eni (Italy) (IT)
  • Institute of Research on Terrestrial Ecosystems, National Council of Research, Via Moruzzi 1, 56124 Pisa, Italy
  • University of Genoa (IT)
Corresponding author
Vocciante, Marco
Venue
Soil Systems
Publisher
MDPI AG
Published
2021-09-03
Volume
5
Issue
3
Pages
55
ISSN
2571-8789 (ISSN-L)
OpenAlex
W3197821679
Cited by
19
References
67
Citations by year
2026: 1 · 2025: 2 · 2024: 3 · 2023: 1 · 2022: 12
FWCI
0.99
Type
journal article
Language
en
Open access
Locations
  • Soil Systems (publishedVersion, cc-by)
  • DOAJ (DOAJ: Directory of Open Access Journals) (submittedVersion, cc-by-sa)
  • CINECA IRIS Institutial Research Information System (University of Genoa) (submittedVersion, other-oa)
Funders
Syndial S.p.A. (3500038857)
Topics
  • Physical Sciences › Environmental Science › Pollution › Heavy metals in environment
  • Life Sciences › Agricultural and Biological Sciences › Plant Science › Plant-Microbe Interactions and Immunity
  • Physical Sciences › Environmental Science › Pollution › Microbial bioremediation and biosurfactants
Keywords
lead phytoextraction, endophytic bacteria, phytoremediation, lead-contaminated soil, EDTA, microbial inoculum, Brassica juncea, sunflower, Sonchus tenerrimus, Bromus sterilis, plant-microbe interactions, heavy metal uptake

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CoChat. (2026). Citation check: Enhanced Lead Phytoextraction by Endophytes from Indigenous Plants. https://app.cochat.ai/papers/10.3390/soilsystems5030055
The paper
Pietrini, I., Grifoni, M., Franchi, E., Cardaci, A., Pedron, F., Barbafieri, M., Petruzzelli, G., & Vocciante, M. (2021). Enhanced Lead Phytoextraction by Endophytes from Indigenous Plants. Soil Systems. https://doi.org/10.3390/soilsystems5030055

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