Phytoremediation potential of Arundo donax (Giant Reed) in contaminated soil by heavy metals.

Environmental remediation Green plants Heavy metals Microorganisms Phytoremediation Soil contamination

Journal

Environmental research
ISSN: 1096-0953
Titre abrégé: Environ Res
Pays: Netherlands
ID NLM: 0147621

Informations de publication

Date de publication:
06 2020
Historique:
received: 02 01 2020
revised: 15 03 2020
accepted: 20 03 2020
pubmed: 5 4 2020
medline: 21 11 2020
entrez: 5 4 2020
Statut: ppublish

Résumé

Soil pollution from heavy metals poses a serious risk for environment and public health. Phytoremediation is an eco-friendly and cheaper alternative compared to chemical-physical techniques. We carried out in vitro tests where three microorganisms Trichoderma harzianum, Saccharomyces cerevisiae and Wickerhamomyces anomalus were exposed to eight different heavy metals (one metal at a time) in order to evaluate resistance, growth and bioaccumulation capability for each metal (Ni, Cd, Cu, V, Zn, As, Pb, Hg). Taking into account the natural characteristics of T. harzianum, (resistance to environmental stress, resistance to pathogenic fungi, ability to establish symbiotic relationships with superior green plants) and the good bioaccumulation capacity for V, As, Cd, Hg, Pb shown after in vitro tests, it was chosen as a microorganism to be used in greenhouse tests. Controlled exposure tests were performed in greenhouse, where Arundo donax and mycorrhized Arundo donax with T. harzianum were exposed for 7 months at two different doses (L1 and L2) of a heavy metal mix, so as to assess whether the symbiotic association could improve the bioaccumulation capability of the superior green plant A. donax. Heavy metals were determined with ICP-MS. The average bioaccumulation percentage values of A. donax for L1 and L2 were, respectively: Ni (31%, 26%); Cd (35%, 50%); Cu (30%, 35%); As (19%, 27%); Pb (18%, 14%); Hg (42%, 45%); V (39%, 26%); Zn (23%, 9%). The average bioaccumulation percentage values of mycorrhized A. donax with T. harzianum for L1 and L2 were, respectively: Ni (27%, 38%); Cd (44%, 42%); Cu (36%, 29%); As (17%, 23%); Pb (37%, 54%); Hg (44%, 60%); V (16%, 20%); Zn (14%, 7%). A. donax showed the highest BAF (bioaccumulation factor) for Cd (0.50), Cu (0.35), As (0.27) and Hg (0.45) after exposure to L2; mycorrhized A. donax with T. harzianum showed the highest BAF for Ni (0.38), Cd (0.42), Pb (0.54) and Hg (0.60) after exposure to L2. A. donax showed the highest TF (translocation factor) values for Cd (0.28) and Hg (0.26) after exposition at L1 and L2 respectively; A. donax mycorrhized with T. harzianum showed the highest TF values for Cd (0.70), As (0.56), V (0.24), Pb (0.18) after exposition at L2, and Zn (0.30) after exposition at L1. Our study showed a good growth capability in contaminated soils and a good bioaccumulation capability of heavy metals, both for A. donax and mycorrhized A. donax with T. harzianum. Furthermore, for three metals (Ni, Pb and Hg) the bioaccumulation capability was improved by the symbiosis of T. harzianum with A. donax. So, these results proved the suitability both for A. donax and mycorrhized A. donax with T. harzianum for phytoremediation processes.

Identifiants

pubmed: 32247150
pii: S0013-9351(20)30320-0
doi: 10.1016/j.envres.2020.109427
pii:
doi:

Substances chimiques

Metals, Heavy 0
Soil 0
Soil Pollutants 0

Types de publication

Journal Article

Langues

eng

Sous-ensembles de citation

IM

Pagination

109427

Informations de copyright

Copyright © 2020 The Authors. Published by Elsevier Inc. All rights reserved.

Déclaration de conflit d'intérêts

Declaration of competing interest The authors declare that there is no conflict of interests regarding the publication of this paper.

Auteurs

Antonio Cristaldi (A)

Environmental and Food Laboratories (LIAA), Department of Medical Science, Surgical and Advanced Technologies "G.F. Ingrassia", University of Catania, Italy.

Gea Oliveri Conti (G)

Environmental and Food Laboratories (LIAA), Department of Medical Science, Surgical and Advanced Technologies "G.F. Ingrassia", University of Catania, Italy. Electronic address: olivericonti@unict.it.

Salvatore Luciano Cosentino (SL)

Department of Agriculture, Food and Environment (Di3A), University of Catania, Italy.

Giovanni Mauromicale (G)

Department of Agriculture, Food and Environment (Di3A), University of Catania, Italy.

Chiara Copat (C)

Environmental and Food Laboratories (LIAA), Department of Medical Science, Surgical and Advanced Technologies "G.F. Ingrassia", University of Catania, Italy.

Alfina Grasso (A)

Environmental and Food Laboratories (LIAA), Department of Medical Science, Surgical and Advanced Technologies "G.F. Ingrassia", University of Catania, Italy.

Pietro Zuccarello (P)

Environmental and Food Laboratories (LIAA), Department of Medical Science, Surgical and Advanced Technologies "G.F. Ingrassia", University of Catania, Italy.

Maria Fiore (M)

Environmental and Food Laboratories (LIAA), Department of Medical Science, Surgical and Advanced Technologies "G.F. Ingrassia", University of Catania, Italy.

Cristina Restuccia (C)

Department of Agriculture, Food and Environment (Di3A), University of Catania, Italy.

Margherita Ferrante (M)

Environmental and Food Laboratories (LIAA), Department of Medical Science, Surgical and Advanced Technologies "G.F. Ingrassia", University of Catania, Italy.

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