Abstract

Abstract. Dry–rewetting perturbations are natural disturbances in the edaphic environment and particularly in dryland cultivation areas. The interaction of this disturbance with glyphosate-based herbicides (GBHs) deserves special attention in the soil environment due to the intensification of agricultural practices and the acceleration of climate change with an intensified water cycle. The objective of this study was to assess the response of microbial communities in a soil with a long history of GBHs to a secondary imposed perturbation (a single dry–rewetting event). A factorial microcosm study was conducted to evaluate the potential conditioning effect of an acute glyphosate exposure on the response to a following dry–rewetting event. A respiratory quotient (RQ) based on an ecologically relevant substrate (p-coumaric acid) and basal respiration was used as a physiological indicator. Similarly, DNA-based analyses were considered, including quantitative PCR (qPCR) of functional sensitive microbial groups linked to cycles of carbon (Actinobacteria) and nitrogen (ammonia-oxidizing microorganisms), qPCR of total bacteria and denaturing gradient gel electrophoresis (DGGE) of ammonia-oxidizing bacteria (AOB). Significant effects of herbicide and of dry–rewetting perturbations were observed in the RQ and in the copy number of the amoA gene of AOB, respectively. However, no significant interaction was observed between them when analyzing the physiological indicator and the copy number of the evaluated genes. PCR–DGGE results were not conclusive regarding a potential effect of dry–rewetting × herbicide interaction on AOB community structure, suggesting further analysis by deep sequencing of the amoA gene. The results of this study indicate that the perturbation of an acute glyphosate exposure in a soil with a long history of this herbicide does not have a conditioning effect on the response to a subsequent dry–rewetting disturbance according to a physiological indicator or the quantified bacterial/archaeal genes. This is particularly relevant for the sustainability of soils in rainfed agriculture, where frequent exposure to GBHs along with intensification of hydrological cycles are expected to occur. Further studies considering multiple dry–rewetting disturbances and in different soil types should be conducted to simulate those conditions and to validate our results.

Highlights

  • Soil microbial communities play a central role in several processes that contribute to a wide range of important ecosystem services (Tilman et al, 2002; EFSA Panel on Plant Protection Products and their Residues, 2016)

  • A rapid rewetting can trigger an osmotic shock-inducing lysis, release of intracellular solutes and an increase in C and N mineralization (Fierer et al, 2003). The interaction of these disturbances with the perturbation imposed by glyphosate-based herbicides (GBHs) has not been assessed before, even when the simultaneous exposure to both factors represents a common scenario in dryland cultivation areas such as in the semiarid Pampas of Argentina

  • We focused on microorganisms with well-known sensitivity to GBHs and other pesticides like ammonia-oxidizing bacteria and archaea (AOB, AOA) (Zhang et al, 2018) and Actinobacteria (Barriuso et al, 2010)

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Summary

Introduction

Soil microbial communities play a central role in several processes that contribute to a wide range of important ecosystem services (Tilman et al, 2002; EFSA Panel on Plant Protection Products and their Residues, 2016). The interaction of these disturbances with the perturbation imposed by glyphosate-based herbicides (GBHs) has not been assessed before, even when the simultaneous exposure to both factors represents a common scenario in dryland cultivation areas such as in the semiarid Pampas of Argentina. These disturbance events could increase their frequency due to the intensification of agricultural practices based on glyphosate-resistant (GR) crops (Cerdeira and Duke, 2006) and repeated dry–rewetting cycles under an accelerating climate change (Huntington, 2006; Evans and Wallenstein, 2011)

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