Differential tolerance to Cd and Zn of arbuscular mycorrhizal (AM) fungal spores isolated from heavy metal-polluted and unpolluted soils

Spores of arbuscular mycorrhizal fungi were isolated from two soils of field trials at INRA-Bordeaux (France) polluted by long-term application of a zinc-polluted sewage sludge (S2 soil) or treated with cadmium nitrate (Cd40 soil) and from corresponding unpolluted soils (F and Cd0 soils). These AM f...

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Veröffentlicht in:Plant and soil 1994-12, Vol.167 (2), p.189-196
Hauptverfasser: Weissenhorn, I. (Centre de Pedologie Biologique CNRS, Vandoeuvre-les-Nancy (France)), Glashoff, A, Leyval, C, Berthelin, J
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container_start_page 189
container_title Plant and soil
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creator Weissenhorn, I. (Centre de Pedologie Biologique CNRS, Vandoeuvre-les-Nancy (France))
Glashoff, A
Leyval, C
Berthelin, J
description Spores of arbuscular mycorrhizal fungi were isolated from two soils of field trials at INRA-Bordeaux (France) polluted by long-term application of a zinc-polluted sewage sludge (S2 soil) or treated with cadmium nitrate (Cd40 soil) and from corresponding unpolluted soils (F and Cd0 soils). These AM fungi were tested for their tolerance to Cd and Zn added as salt solutions with increasing concentrations (0 to 10 mg L⁻¹) in a simple spore germination device. According to preliminary identification the predominant species in S2 and F cultures was Glomus mosseae, whereas Cd40 and Cd0 cultures contained a mixture of at least G. mosseae and G. etunicatum. Germination of Cd40 spores was more tolerant to Cd and Zn than for Cd0 spores, with EC₅₀ values of 73 and 158 µmol L⁻¹ added Cd and Zn corresponding to approximately 10 and 13 µmol L⁻¹ remaining in solution in the device. The S2 spores from the sludge contaminated soil were more tolerant to Zn (EC₅₀ = 87 µmol L⁻¹ but not to Cd (EC₅₀ = 7.5 µmol L⁻¹ than the spores from the farmyard manure-treated F soil (EC₅₀ = 38 and 8.8 µmol L⁻¹ respectively). Thus, S2 culture exhibited a specific tolerance to Zn, which was lower than the unspecific tolerance of Cd40 culture to both Cd and Zn, despite the much higher Zn availability in S2 soil. These results indicate that AM fungi from different soils may differ in their metal susceptibility and that both metal specific and unspecific tolerance mechanisms may be selected in metal polluted soils.
doi_str_mv 10.1007/bf00007944
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(Centre de Pedologie Biologique CNRS, Vandoeuvre-les-Nancy (France)) ; Glashoff, A ; Leyval, C ; Berthelin, J</creator><creatorcontrib>Weissenhorn, I. (Centre de Pedologie Biologique CNRS, Vandoeuvre-les-Nancy (France)) ; Glashoff, A ; Leyval, C ; Berthelin, J</creatorcontrib><description>Spores of arbuscular mycorrhizal fungi were isolated from two soils of field trials at INRA-Bordeaux (France) polluted by long-term application of a zinc-polluted sewage sludge (S2 soil) or treated with cadmium nitrate (Cd40 soil) and from corresponding unpolluted soils (F and Cd0 soils). These AM fungi were tested for their tolerance to Cd and Zn added as salt solutions with increasing concentrations (0 to 10 mg L⁻¹) in a simple spore germination device. According to preliminary identification the predominant species in S2 and F cultures was Glomus mosseae, whereas Cd40 and Cd0 cultures contained a mixture of at least G. mosseae and G. etunicatum. Germination of Cd40 spores was more tolerant to Cd and Zn than for Cd0 spores, with EC₅₀ values of 73 and 158 µmol L⁻¹ added Cd and Zn corresponding to approximately 10 and 13 µmol L⁻¹ remaining in solution in the device. The S2 spores from the sludge contaminated soil were more tolerant to Zn (EC₅₀ = 87 µmol L⁻¹ but not to Cd (EC₅₀ = 7.5 µmol L⁻¹ than the spores from the farmyard manure-treated F soil (EC₅₀ = 38 and 8.8 µmol L⁻¹ respectively). Thus, S2 culture exhibited a specific tolerance to Zn, which was lower than the unspecific tolerance of Cd40 culture to both Cd and Zn, despite the much higher Zn availability in S2 soil. 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These results indicate that AM fungi from different soils may differ in their metal susceptibility and that both metal specific and unspecific tolerance mechanisms may be selected in metal polluted soils.</description><subject>Acid soils</subject><subject>Agricultural site preparation</subject><subject>Agricultural soils</subject><subject>Agronomy. Soil science and plant productions</subject><subject>Animal, plant and microbial ecology</subject><subject>Applied ecology</subject><subject>Biological and medical sciences</subject><subject>CADMIO</subject><subject>CADMIUM</subject><subject>CHEMICAL RESISTANCE</subject><subject>CINC</subject><subject>Ecotoxicology, biological effects of pollution</subject><subject>Fundamental and applied biological sciences. 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(Centre de Pedologie Biologique CNRS, Vandoeuvre-les-Nancy (France))</creatorcontrib><creatorcontrib>Glashoff, A</creatorcontrib><creatorcontrib>Leyval, C</creatorcontrib><creatorcontrib>Berthelin, J</creatorcontrib><collection>AGRIS</collection><collection>Pascal-Francis</collection><collection>CrossRef</collection><collection>Ecology Abstracts</collection><collection>Industrial and Applied Microbiology Abstracts (Microbiology A)</collection><collection>Pollution Abstracts</collection><collection>Technology Research Database</collection><collection>Environmental Sciences and Pollution Management</collection><collection>Engineering Research Database</collection><collection>Algology Mycology and Protozoology Abstracts (Microbiology C)</collection><collection>Biotechnology and BioEngineering Abstracts</collection><jtitle>Plant and soil</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Weissenhorn, I. 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These AM fungi were tested for their tolerance to Cd and Zn added as salt solutions with increasing concentrations (0 to 10 mg L⁻¹) in a simple spore germination device. According to preliminary identification the predominant species in S2 and F cultures was Glomus mosseae, whereas Cd40 and Cd0 cultures contained a mixture of at least G. mosseae and G. etunicatum. Germination of Cd40 spores was more tolerant to Cd and Zn than for Cd0 spores, with EC₅₀ values of 73 and 158 µmol L⁻¹ added Cd and Zn corresponding to approximately 10 and 13 µmol L⁻¹ remaining in solution in the device. The S2 spores from the sludge contaminated soil were more tolerant to Zn (EC₅₀ = 87 µmol L⁻¹ but not to Cd (EC₅₀ = 7.5 µmol L⁻¹ than the spores from the farmyard manure-treated F soil (EC₅₀ = 38 and 8.8 µmol L⁻¹ respectively). Thus, S2 culture exhibited a specific tolerance to Zn, which was lower than the unspecific tolerance of Cd40 culture to both Cd and Zn, despite the much higher Zn availability in S2 soil. These results indicate that AM fungi from different soils may differ in their metal susceptibility and that both metal specific and unspecific tolerance mechanisms may be selected in metal polluted soils.</abstract><cop>Dordrecht</cop><pub>Kluwer Academic Publishers</pub><doi>10.1007/bf00007944</doi><tpages>8</tpages></addata></record>
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identifier ISSN: 0032-079X
ispartof Plant and soil, 1994-12, Vol.167 (2), p.189-196
issn 0032-079X
1573-5036
language eng
recordid cdi_proquest_miscellaneous_16746135
source JSTOR Archive Collection A-Z Listing; SpringerLink Journals - AutoHoldings
subjects Acid soils
Agricultural site preparation
Agricultural soils
Agronomy. Soil science and plant productions
Animal, plant and microbial ecology
Applied ecology
Biological and medical sciences
CADMIO
CADMIUM
CHEMICAL RESISTANCE
CINC
Ecotoxicology, biological effects of pollution
Fundamental and applied biological sciences. Psychology
Fungal spores
Fungi
Germination
GLOMUS
Heavy metals
Microbial ecology
MYCORHIZE
MYCORRHIZAE
POLLUTION DU SOL
POLUCION DEL SUELO
RESISTANCE AUX PRODUITS CHIMIQUES
RESISTENCIA QUIMICA
Soil
Soil and water pollution
Soil fungi
SOIL POLLUTION
Soil science
Spore germination
Terrestrial environment, soil, air
ZINC
title Differential tolerance to Cd and Zn of arbuscular mycorrhizal (AM) fungal spores isolated from heavy metal-polluted and unpolluted soils
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