ABSTRACT
Abstract The Riachuelo river basin (RRB) is considered one of the most polluted environments in the world. Knowledge of arbuscular mycorrhizal fungi (AMF) adapted to this extremely polluted environment is important for the establishment of future soil restoration projects. This work aims to make a first list of AMF species present on the RRB. Soil and root samples were randomly taken in an area of approximately 1500 m2, mycorrhization percentages were evaluated. AMF species were detected by molecular and morphological techniques. Sixteen AMF morphological species and 64 molecular species were reported in this work. Dominikia iranica, Funneliformis constrictum, Funneliformis mosseae, Rhizophagus intraradices, Rhizophagus irregularis and Septoglomus viscosum were detected by both techniques while Claroideoglomus sp. was only detected by pyrosequencing. The list of species reported in this work represents the first description of the RRB AMF community.
Resumen La cuenca del río Riachuelo (CRR) es considerada uno de los ambientes más contaminados del mundo. Conocer los hongos formadores de micorrizas arbusculares (HFMA) adaptados a este ambiente extremadamente contaminado es importante para el establecimiento de futuros proyectos de restauración de suelos. Este trabajo se propuso hacer una primera lista de especies de HFMA presentes en la CRR. Se tomaron muestras de suelo y raíces al azar en un área de aproximadamente 1500 m2 y se evaluaron los porcentajes de micorrización. La identificación de especies de HFMA se basó en técnicas moleculares y morfológicas. Se detectaron 16 especies morfológicas y 64 especies moleculares de HFMA. Dominikia iranica, Funneliformis constrictum, Funneliformis mosseae, Rhizophagus intraradices, Rhizophagus irregularis y Septoglomus viscosum se detectaron mediante ambas técnicas, mientras que Claroideoglomus sp. solo fue detectado por pirosecuenciación. La lista de especies reportada en este trabajo representa la primera descripción de la comunidad de HFMA de la CRR.
ABSTRACT
The Riachuelo river basin (RRB) is considered one of the most polluted environments in the world. Knowledge of arbuscular mycorrhizal fungi (AMF) adapted to this extremely polluted environment is important for the establishment of future soil restoration projects. This work aims to make a first list of AMF species present on the RRB. Soil and root samples were randomly taken in an area of approximately 1500m2, mycorrhization percentages were evaluated. AMF species were detected by molecular and morphological techniques. Sixteen AMF morphological species and 64 molecular species were reported in this work. Dominikia iranica, Funneliformis constrictum, Funneliformis mosseae, Rhizophagus intraradices, Rhizophagus irregularis and Septoglomus viscosum were detected by both techniques while Claroideoglomus sp. was only detected by pyrosequencing. The list of species reported in this work represents the first description of the RRB AMF community.
Subject(s)
Environmental Pollution , Metals, Heavy , Mycorrhizae/isolation & purification , Soil Microbiology , Soil Pollutants , Argentina , RiversABSTRACT
The commercial use of genetically modified (GM) plants has significantly increased worldwide. The interactions between GM plants and arbuscular mycorrhizal (AM) fungi are of considerable importance given the agricultural and ecological role of AM and the lack of knowledge regarding potential effects of drought-tolerant GM corn ( L.) on AM fungal symbiosis. This work studied AM fungal colonization in five corn lines growing under two different irrigation regimes (30 and 100% of soil field capacity [SFC]). Four of the lines were GM corn, and two of these were drought tolerant. The experiment was conducted for 60 d in a growth chamber under constant irrigation, after which mycorrhization, corn biomass, and days to plant senescence (DTS) were evaluated. Arbuscular mycorrhizal fungal species of the order were predominant in the soil inocula. At the end of the experiment, all plants showed AM colonization. Mycorrhization was higher at 30% SFC than at 100% SFC. Within the same corn line, the AM fungi produced more vesicles in plant roots under drought stress. Among treatments, DTS varied significantly, and drought-tolerant GM corn lines survived longer than the wild-type corn when maintained at 100% SFC. Corn biomass did not vary among treatments, and no correlations were found between DTS or biomass and mycorrhization. We conclude that overexpression of the gene in corn plants under the experimental conditions of this study did not affect AM fungal infectivity and improved the tolerance of the corn to drought stress.
