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Irrigation of radish (Raphanus sativus L.) with microcystin-enriched water holds low risk for plants and their associated rhizopheric and epiphytic microbiome

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Autore
Petrou M., Karas P.A., Vasileiadis S., Zafiriadis I., Papadimitriou T., Levizou E., Kormas K., Karpouzas D.G.
Data
2020
Language
en
DOI
10.1016/j.envpol.2020.115208
Soggetto
Agricultural robots
Health
Health risks
Irrigation
Microorganisms
Nitrification
Physiology
Soils
Water
Abiotic stressors
Agricultural land
Cyanobacterial blooms
Ecological quality
Freshwater systems
Inhibitory effect
Microbial communities
Rhizospheric soils
Reservoirs (water)
fresh water
microcystin LR
tap water
microcystin
water
algal bloom
bioaccumulation
cyanobacterium
epiphyte
irrigation
rhizosphere
risk assessment
vegetable
abiotic stress
amplicon
Article
bacterial phenomena and functions
biotic stress
consumer
controlled study
ecology
epiphyte
freshwater environment
gene sequence
health hazard
homeostasis
irrigation (agriculture)
Karla reservoir
methylotrophy
microbial community
nitrifyer
plant growth
plant physiology
plant root
radish
real time polymerase chain reaction
rhizosphere bacterium
rhizosphere fungus
risk assessment
soil
soil microflora
species diversity
water supply
water treatment
cyanobacterium
microflora
Raphanus
Greece
Karla Lake
Magnesia
Thessaly
Bacteria (microorganisms)
Cyanobacteria
Raphanus sativus
Cyanobacteria
Microbiota
Microcystins
Raphanus
Water
Elsevier Ltd
Mostra tutti i dati dell'item
Abstract
Microcystins (MCs) are toxins produced during cyanobacterial blooms. They reach soil and translocated to plants through irrigation of agricultural land with water from MC-impacted freshwater systems. To date we have good understanding of MC effects on plants, but not for their effects on plant-associated microbiota. We tested the hypothesis that MC-LR, either alone or with other stressors present in the water of the Karla reservoir (a low ecological quality and MC-impacted freshwater system), would affect radish plants and their rhizospheric and phyllospheric microbiome. In this context a pot experiment was employed where radish plants were irrigated with tap water without MC-LR (control) or with 2 or 12 μg L−1 of pure MC-LR (MC2 and MC12), or water from the Karla reservoir amended (12 μg L−1) or not with MC-LR. We measured MC levels in plants and rhizospheric soil and we determined effects on (i) plant growth and physiology (ii) the nitrifying microorganisms via q-PCR, (ii) the diversity of bacterial and fungal rhizospheric and epiphytic communities via amplicon sequencing. MC-LR and/or Karla water treatments resulted in the accumulation of MC in taproot at levels (480–700 ng g−1) entailing possible health risks. MC did not affect plant growth or physiology and it did not impose a consistent inhibitory effect on soil nitrifiers. Karla water rather than MC-LR was the stronger determinant of the rhizospheric and epiphytic microbial communities, suggesting the presence of biotic or abiotic stressors, other than MC-LR, in the water of the Karla reservoir which affect microorganisms with a potential role (i.e. pathogens inhibition, methylotrophy) in the homeostasis of the plant-soil system. Overall, our findings suggest that MC-LR, when applied at environmentally relevant concentrations, is not expected to adversely affect the radish-microbiota system but might still pose risk for consumers’ health. © 2020 Elsevier LtdIrrigation of radish with water containing MC-LR, at environmental relevant levels, does not affect the radish rhizospheric and phyllospheric microbiota but poses a risk for consumers’ health. © 2020 Elsevier Ltd
URI
http://hdl.handle.net/11615/78188
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  • Δημοσιεύσεις σε περιοδικά, συνέδρια, κεφάλαια βιβλίων κλπ. [19735]

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