首页> 外文期刊>Tree Physiology >Nickel-tolerant ectomycorrhizal Pisolithus albus ultramafic ecotype isolated from nickel mines in New Caledonia strongly enhance growth of the host plant Eucalyptus globulus at toxic nickel concentrations
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Nickel-tolerant ectomycorrhizal Pisolithus albus ultramafic ecotype isolated from nickel mines in New Caledonia strongly enhance growth of the host plant Eucalyptus globulus at toxic nickel concentrations

机译:从新喀里多尼亚的镍矿中分离出的耐镍外生菌根Pisolithus albus超镁铁质生态型在有毒镍浓度下强烈促进寄主植物桉树的生长

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摘要

Ectomycorrhizal (ECM) Pisolithus albus (Cooke & Massee), belonging to the ultramafic ecotype isolated in nickel-rich serpentine soils from New Caledonia (a tropical hotspot of biodiversity) and showing in vitro adaptive nickel tolerance, were inoculated to Eucalyptus globulus Labill used as a Myrtaceae plant-host model to study ectomycorrhizal symbiosis. Plants were then exposed to a nickel (Ni) dose–response experiment with increased Ni treatments up to 60 mg kg − 1 soil as extractable Ni content in serpentine soils. Results showed that plants inoculated with ultramafic ECM P. albus were able to tolerate high and toxic concentrations of Ni (up to 60 μg g − 1) while uninoculated controls were not. At the highest Ni concentration tested, root growth was more than 20-fold higher and shoot growth more than 30-fold higher in ECM plants compared with control plants. The improved growth in ECM plants was associated with a 2.4-fold reduction in root Ni concentration but a massive 60-fold reduction in transfer of Ni from root to shoots. In vitro, P. albus strains could withstand high Ni concentrations but accumulated very little Ni in its tissue. The lower Ni uptake by mycorrhizal plants could not be explained by increased release of metal-complexing chelates since these were 5- to 12-fold lower in mycorrhizal plants at high Ni concentrations. It is proposed that the fungal sheath covering the plant roots acts as an effective barrier to limit transfer of Ni from soil into the root tissue. The degree of tolerance conferred by the ultramafic P. albus isolates to growth of the host tree species is considerably greater than previously reported for other ECM. The primary mechanisms underlying this improved growth were identified as reduced Ni uptake into the roots and markedly reduced transfer from root to shoot in mycorrhizal plants. The fact that these positive responses were observed at Ni concentrations commonly observed in serpentinic soils suggests that ultramafic ecotypes of P. albus could play an important role in the adaptation of tree species to soils containing high concentrations of heavy metals and aid in strategies for ecological restoration.
机译:Ectomycorrhizal(ECM)Pisolithus albus(Cooke&Massee),属于从新喀里多尼亚(热带生物多样性的热点)富含镍的蛇纹石土壤中分离出的超镁铁质生态型,并显示出体外适应性镍耐受性,被接种到球状桉(Eucalyptus globulus Labill)上。桃金娘科植物宿主模型研究外生菌根共生。然后将植物暴露于镍(Ni)剂量-反应实验,增加镍处理量至60 mg kg - 1 土壤作​​为可吸收的蛇纹土。结果表明,接种超铁质ECM P. albus的植物能够耐受高浓度和高毒性的Ni(高达60μgg - 1 ),而未接种的对照则不能。与对照植物相比,在测试的最高Ni浓度下,ECM植物的根生长高出20倍以上,而枝条生长高出30倍以上。 ECM植物生长的改善与根部Ni浓度降低2.4倍有关,但Ni从根部转移到枝条上的Ni转移大量降低了60倍。在体外,P。albus菌株可以承受较高的Ni浓度,但在其组织中几乎不累积Ni。不能通过金属复合螯合物的释放增加来解释菌根植物对镍的吸收较低,因为在高Ni浓度下,这些元素在菌根植物中降低了5至12倍。提出覆盖植物根部的真菌鞘用作限制Ni从土壤向根组织中转移的有效屏障。超基质细胞假单胞菌分离物赋予宿主树种生长的耐受程度比以前报道的其他ECM耐受性要高得多。鉴定出这种改善生长的主要机理是:在菌根植物中减少了镍对根的吸收,并显着减少了从根到芽的转移。这些阳性反应是在蛇形土壤中通常观察到的镍浓度下观察到的事实表明,超镁铁质生态型的P. albus可能在树木物种适应高浓度重金属的土壤中起重要作用,并有助于生态修复策略。

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  • 来源
    《Tree Physiology》 |2010年第10期|p.1311-1319|共9页
  • 作者单位

    Laboratoire des Symbioses Tropicales et Méditerranéennes (LSTM), UMR 113 CIRAD/INRA/IRD/SupAgro/UMII, Centre IRD, BPA5, Promenade Roger Laroque, 98848 Nouméa cedex, Nouvelle-Calédonie|Corresponding author ( philippe.jourand{at}ird.fr);

    Laboratoire des Symbioses Tropicales et Méditerranéennes (LSTM), UMR 113 CIRAD/INRA/IRD/SupAgro/UMII, Centre IRD, BPA5, Promenade Roger Laroque, 98848 Nouméa cedex, Nouvelle-Calédonie|Institut Agronomique néo-Calédonien, Nouméa, Nouvelle-Calédonie;

    School of Earth and Environmental Sciences, University of Adelaide, Adelaide 5005, Australia;

    Laboratoire des Symbioses Tropicales et Méditerranéennes (LSTM), UMR 113 CIRAD/INRA/IRD/SupAgro/UMII, Centre IRD, BPA5, Promenade Roger Laroque, 98848 Nouméa cedex, Nouvelle-Calédonie;

    Laboratoire Insulaire du Vivant et de l'Environnement, Université de la Nouvelle-Calédonie, BPR4, 98851 Nouméa Cedex, Nouvelle-Calédonie;

    Laboratoire des Symbioses Tropicales et Méditerranéennes (LSTM), UMR 113 CIRAD/INRA/IRD/SupAgro/UMII, Centre IRD, BPA5, Promenade Roger Laroque, 98848 Nouméa cedex, Nouvelle-Calédonie;

    Laboratoire des Symbioses Tropicales et Méditerranéennes (LSTM), UMR 113 CIRAD/INRA/IRD/SupAgro/UMII, TA A-82/J Campus International de Baillarguet, 34398 Montpellier cedex 5, France;

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