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. 2021 Jun 29;6(3):e0036021.
doi: 10.1128/mSystems.00360-21. Epub 2021 Jun 8.

Computational Model To Quantify the Growth of Antibiotic-Resistant Bacteria in Wastewater

Affiliations

Computational Model To Quantify the Growth of Antibiotic-Resistant Bacteria in Wastewater

Indorica Sutradhar et al. mSystems. .

Abstract

Although wastewater and sewage systems are known to be significant reservoirs of antibiotic-resistant bacterial populations and periodic outbreaks of drug-resistant infection, there is little quantitative understanding of the drivers behind resistant population growth in these settings. In order to fill this gap in quantitative understanding of the development of antibiotic-resistant infections in wastewater, we have developed a mathematical model synthesizing many known drivers of antibiotic resistance in these settings to help predict the growth of resistant populations in different environmental scenarios. A number of these drivers of drug-resistant infection outbreak, including antibiotic residue concentration, antibiotic interaction, chromosomal mutation, and horizontal gene transfer, have not previously been integrated into a single computational model. We validated the outputs of the model with quantitative studies conducted on the eVOLVER continuous culture platform. Our integrated model shows that low levels of antibiotic residues present in wastewater can lead to increased development of resistant populations and that the dominant mechanism of resistance acquisition in these populations is horizontal gene transfer rather than acquisition of chromosomal mutations. Additionally, we found that synergistic antibiotics at low concentrations lead to increased resistant population growth. These findings, consistent with recent experimental and field studies, provide new quantitative knowledge on the evolution of antibiotic-resistant bacterial reservoirs, and the model developed herein can be adapted for use as a prediction tool in public health policy making, particularly in low-income settings where water sanitation issues remain widespread and disease outbreaks continue to undermine public health efforts. IMPORTANCE The rate at which antimicrobial resistance (AMR) has developed and spread throughout the world has increased in recent years, and according to the Review on Antimicrobial Resistance in 2014, it is suggested that the current rate will lead to AMR-related deaths of several million people by 2050 (Review on Antimicrobial Resistance, Tackling a Crisis for the Health and Wealth of Nations, 2014). One major reservoir of resistant bacterial populations that has been linked to outbreaks of drug-resistant bacterial infections but is not well understood is in wastewater settings, where antibiotic pollution is often present. Using ordinary differential equations incorporating several known drivers of resistance in wastewater, we find that interactions between antibiotic residues and horizontal gene transfer significantly affect the growth of resistant bacterial reservoirs.

Keywords: antibiotic resistance; mathematical modeling; wastewater.

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Figures

FIG 1
FIG 1
Inputs and outputs for preliminary model of antibiotic resistance development in a single bacterial species in a wastewater setting. ARG, antibiotic resistance gene.
FIG 2
FIG 2
Measured susceptible and resistant populations from eVOLVER experiments of E. coli grown in continuous culture in media containing 6 mg/liter rifampicin (a), 8 mg/liter rifampicin (b), and 12 mg/liter rifampicin (c). Postadjustment model outputs in arbitrary units (a.u.) for susceptible and resistant populations of E. coli grown in media containing 6 mg/liter rifampicin (d), 8 mg/liter rifampicin (e), and 12 mg/liter rifampicin (f).
FIG 3
FIG 3
Postadjustment model predictions for susceptible and resistant populations of E. coli grown in media containing 3 mg/liter rifampicin (a) and 10 mg/liter rifampicin (b). Measured susceptible and resistant populations from eVOLVER experiments of E. coli grown in continuous culture in media containing 3 mg/liter rifampicin (c) and 10 mg/liter rifampicin (d).
FIG 4
FIG 4
Sensitive and resistant populations under resistance only from chromosomal mutations (a) and resistance only from the HGT of resistance-conferring plasmids (multidrug-resistant [MDR] plasmid) (b).
FIG 5
FIG 5
Sensitive and resistant populations under antibiotic residue concentrations of 0.5 μg/ml antibiotic 1 plus 0.5 μg/ml antibiotic 2 (a), 1 μg/ml antibiotic 1 plus 1 μg/ml antibiotic 2 (b), and 2 μg/ml antibiotic 1 plus 2 μg/ml antibiotic 2 (c). Time is shown in arbitrary units (a.u).
FIG 6
FIG 6
Effect of horizontal gene transfer rate on time to resistant population dominance for subinhibitory antibiotic residue concentrations (defined as time when Rm + Rp > S).
FIG 7
FIG 7
Effect of bacterial killing rate on time to resistant population dominance for subinhibitory antibiotic residue concentrations (defined as time when Rm + Rp > S).
FIG 8
FIG 8
Effect of synergy of antibiotic combinations on time to resistant population elimination for suprainhibitory antibiotic residue concentrations (a) and time to resistant population dominance for subinhibitory antibiotic residue concentrations (defined as time when Rm + Rp > S) (b).
FIG 9
FIG 9
Sensitive and resistant populations under selective pressure from antimicrobial combination therapy including chromosomal mutation and HGT resistance mechanisms.
FIG 10
FIG 10
Augmented model of sensitive, semiresistant, and resistant populations under selective pressure from rifampicin therapy including only chromosomal mutation mechanisms.

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