Search

Excessive use of herbicides decreases soil biodiversity and fertility. The literature on the xenobiotic response by microorganisms is focused on herbicide biodegradation as a selective event. Non-degradation systems independent of selection could allow the survival of tolerant bacteria in contaminated environments, impacting xenobiotic turnover and, consequently, bioremediation strategies. However, it is uncertain whether the response based on these systems requires selective pressure to be effective. The objective here was to analyze non-degradation phenotypes, enzymatic and structural response systems, of

Herbicides are widely used in agricultural practices for preventing the proliferation of weeds that compete with crops for survival. Upon reaching soil and water, herbicides can damage nontarget organisms, such as bacteria, which need an efficient defense mechanism to tolerate the stress induced by herbicides. 2,4-Dichlorophenoxyacetic acid (2,4-D) is a herbicide that exerts increased oxidative stress among bacterial communities that consequently witness an increased toxicity in their microenvironments. Bacterial isolates were obtained from the biofilm of water that was contaminated with 2,4-D. This biofilm originated from the tanks containing washing water from the packaging of different pesticides, including 2,4-D. Moreover, several isolates were sensitive to biofilm toxicity; however, they remained alive in the presence of 2,4-D. The Pseudomonas sp. CMA-7.3 was selected because of its tolerance against biofilm agrochemicals. Therefore, the objective of this study is to evaluate the antioxidative response system of the Pseudomonas sp. CMA-7.3. This study also analyzed poorly evaluated enzymes, such as superoxide dismutase (SOD), catalase (CAT), ascorbate peroxidase (APX), and guaiacol peroxidase GPX, in the bacterial systems. The toxic effects of 2,4-D on bacteria were evaluated using mechanisms indicating oxidative stress, such as growth curve, cell viability, peroxide, and malondialdehyde. The Pseudomonas sp. CMA-7.3 was an efficient response system against the activity of antioxidant enzymes such as SOD, CAT, APX, and GPX in balancing the production of H2O2, even at high doses as 25x the field dose of the herbicide, thereby proving the toxicity of 2,4-D for this strain and showing the ability of the strain to tolerate 2,4-D. The adaptation of this microorganism to herbicide exposure is truly relevant for improving future metabolic studies on bacterial communities. The strain showed a great potential in the application and developmental prospects of a new product in the bioremediation process of environments contaminated by these herbicides.

Agriculture uses many food production chains, and herbicides participate in this process by eliminating weeds through different biochemical strategies. However, herbicides can affect non-target organisms such as bacteria, which can suffer damage if there is no efficient control of reactive oxygen species. It is not clear, according to the literature, whether the efficiency of this control needs to be selected by the presence of xenobiotics. Thus, the Pseudomonas sp. CMA 6.9 strain, collected from biofilms in an herbicide packaging washing tank, was selected for its tolerance to pesticides and analyzed for activities of different antioxidative enzymes against the herbicides Boral®, absent at the isolation site, and Heat®, present at the site; both herbicides have the same mode of action, the inhibition of the enzyme protoporphyrinogen oxidase. The strain showed tolerance to both herbicides in doses up to 45 times than those applied in agriculture. The toxicity of these herbicides, which is greater for Boral®, was assessed by means of oxidative stress indicators, growth kinetics, viability, and amounts of peroxide and malondialdehyde. However, the studied strain showed two characteristic antioxidant response systems for each herbicide: glutathione-s-transferase acting to control malondialdehyde in treatments with Boral®; and catalase, ascorbate peroxidase, and guaiacol peroxidase in the control of peroxide induced by Heat®. It is possible that this modulation of the activity of different enzymes independent of previous selection characterizes a system of metabolic plasticity that may be more general in the adaptation of microorganisms in soil and water environments subjected to chemical contaminants. This is relevant to the impact of pesticides on the diversity and abundance of microbial species as well as a promising line of metabolic studies in microbial consortia for use in bioremediation.

Herbicides have harmful effects on bacteria, despite not being their primary targets. Herbicide active molecules cause unspecific oxidative stress, affecting soil microbiome function. Microorganisms possess enzymatic and non-enzymatic oxidative stress control systems that enable them to survive in contaminated environments. It is uncertain whether these systems require specific selective pressures to remain effective against contaminants and how the toxicity is signaled. The objective of this work was to analyze the antioxidant enzymes and lipid profiles of a Pseudomonas fluorescens strain, isolated from water used in washing of pesticide containers, as response systems to the herbicide glyphosate, not present at the isolation site. The bacteria showed low growth rates, cell viability and high hydrogen peroxide quantities at 40x and 50x glyphosate concentrations used in agriculture. These findings demonstrate the toxicity of this herbicide to Pseudomonas strain. However, growth rates in the presence of up to 10x were equivalent to the control group, probably because of superoxide dismutase and the catalase isoenzyme activities that managed to maintain peroxide levels under control in the early- and mid-log phases. Identification and quantification of lipids, by gas chromatography and mass spectrometry, showed that specific fatty acids were correlated with high concentrations of glyphosate and specific growth phases in P. fluorescens , through Principal Component Analysis, suggesting a role in modulating responses to glyphosate toxicity. Nevertheless, glyphosate was not present in the isolation site and, therefore, was not previously selective for P. fluorescens . This suggest that the response system is generalist, based on physiological plasticity, indicating substantial adaptative values in environments subjected to intense pesticide contamination. A matter that emerges is what would be the consequences of a system that is able to respond to toxic substances to which soil microbiomes have not had contact on for bacterial diversity and functionality in agricultural soils.