Abstract

Nowadays, the most significant consequence of climate change is drought stress. Drought is one of the important, alarming, and hazardous abiotic stresses responsible for the alterations in soil environment affecting soil organisms, including microorganisms and plants. It alters the activity and functional composition of soil microorganisms that are responsible for crucial ecosystem functions and services. These stress conditions decrease microbial abundance, disturb microbial structure, decline microbial activity, including enzyme production (e.g., such as oxidoreductases, hydrolases, dehydrogenase, catalase, urease, phosphatases, β-glucosidase) and nutrient cycling, leading to a decrease in soil fertility followed by lower plant productivity and loss in economy. Interestingly, the negative effects of drought on soil can be minimized by adding organic substances such as compost, sewage slugs, or municipal solid waste that increases the activity of soil enzymes. Drought directly affects plant morphology, anatomy, physiology, and biochemistry. Its effect on plants can also be observed by changes at the transcriptomic and metabolomic levels. However, in plants, it can be mitigated by rhizosphere microbial communities, especially by plant growth-promoting bacteria (PGPB) and fungi (PGPF) that adapt their structural and functional compositions to water scarcity. This review was undertaken to discuss the impacts of drought stress on soil microbial community abundance, structure and activity, and plant growth and development, including the role of soil microorganisms in this process. Microbial activity in the soil environment was considered in terms of soil enzyme activities, pools, fluxes, and processes of terrestrial carbon (C) and nitrogen (N) cycles. A deep understanding of many aspects is necessary to explore the impacts of these extreme climate change events. We also focus on addressing the possible ways such as genome editing, molecular analysis (metagenomics, transcriptomics, and metabolomics) towards finding better solutions for mitigating drought effects and managing agricultural practices under harsh condition in a profitable manner.

Highlights

  • An increase in greenhouse gases, such as carbon dioxide (CO2), methane (CH4), and nitrous oxide (N2O), and atmospheric temperature, and depletion of water resources, being a consequence of anthropogenic activities, have driven climate change [1,2,3,4,5]

  • Authors speculated that the decrease in Gram-positive biomarker abundance after treatment with all three phytohormones indicates drought-adapted bacteria that responded negatively to stress signaling by investing resources in survival strategies such as dormancy, osmolytes, or spore production instead of growth and turnover

  • Siebielec et al [12] showed that after one month drought period, the nitrification potential (NP) activity was reduced by 70 and 80% in the loamy and sandy soils, respectively. These results indicate that the resistance of sandy soil with low organic matter content to drought stress was lower than that in loamy soil

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Summary

Introduction

An increase in greenhouse gases, such as carbon dioxide (CO2), methane (CH4), and nitrous oxide (N2O), and atmospheric temperature, and depletion of water resources, being a consequence of anthropogenic activities, have driven climate change [1,2,3,4,5]. Climate change scenarios predict a further decrease in average precipitation from May to October [12] These trends show that the risk of soil drought in the vegetation growing season is high and may negatively affect crop yields. Despite negative aspects of changes caused by drought, such severe environmental conditions can induce interesting adaptations in microbes and plants that allow them to survive and reproduce. These adaptations can lead to the emergence of new functional groups in the ecosystem or serve as an important tool for improving agricultural practices and plant breeding programs [4,25]. A deep uinncdluedrsitnagndthinegroolef omf asoniyl masipcreocotsrgiasnnisemcessisnartyhitsopreoxcpelsosr.eAthdeeeipmupnacdtesrsotfanthdeinseg oexf tmreamnye calsipmeacttes icshnanecgeesseavreynttos.explore the impacts of these extreme climate change events

Impact of Drought Stress on Microbial Communities and Enzyme Activities
Effect of Drought on Soil Enzyme Activities
Effect of Drought on Microbial Activity
Mitigation of Drought Effects on Microbial Activity by Soil Amendments
Physiological and Biochemical Changes in Plants in Response to Drought Stress
Transcriptomic and Metabolomic Changes in Plants under Drought Stress
Identification of Differential Co-expression Modules
Co-localization of DEGs with QTL Intervals
Findings
Conclusions and Further Perspectives
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