Scope of Antibiotic Resistance Genes in Sewage Sludge for Therapeutic Uses

Author(s):  
Parul Chaudhary ◽  
Heena Parveen ◽  
Anuj Chaudhary ◽  
Murtaza Ali ◽  
Devika Gautam ◽  
...  
2020 ◽  
Author(s):  
David Calderón-Franco ◽  
Apoorva Seeram ◽  
Gertjan Medema ◽  
Mark C. M. van Loosdrecht ◽  
David G. Weissbrodt

AbstractDisinfection of treated wastewater in wastewater treatment plants (WWTPs) is used to minimize emission of coliforms, pathogens, and antibiotic resistant bacteria (ARB) in the environment. However, the fate of free-floating extracellular DNA (eDNA) that do carry antibiotic resistance genes (ARGs) and mobile genetic elements (MGEs) is overlooked. Water technologies are central to urban and industrial ecology for sanitation and resource recovery. Biochar produced by pyrolysis of sewage sludge and iron-oxide-coated sands recovered as by-product of drinking water treatment were tested as adsorbents to remove ARGs and MGEs from WWTP effluent. DNA adsorption properties and materials applicability were studied in batch and up-flow column systems at bench scale. Breakthrough curves were measured with ultrapure water and treated wastewater at initial DNA concentrations of 0.1-0.5 mg mL-1 and flow rates of 0.1-0.5 mL min-1. Batch tests with treated wastewater indicated that the adsorption profiles of biochar and iron-oxide coated sand followed a Freundlich isotherm, suggesting a multilayer adsorption of nucleic acids. Sewage-sludge biochar exhibited higher DNA adsorption capacity (1 mg g-1) and longer saturation breakthrough times (4 to 10 times) than iron-oxide coated sand (0.2 mg g-1). The removal of a set of representative ARGs and MGEs was measured by qPCR comparing the inlet and outlet of the plug-flow column fed with treated wastewater. ARGs and MGEs present as free-floating eDNA were adsorbed by sewage-sludge biochar at 85% and iron-oxide coated sand at 54%. From the environmental DNA consisting of the free-floating extracellular DNA plus the intracellular DNA of the cells present in the effluent water, 97% (sewage-sludge biochar) and 66% (iron-oxide coated sand) of the tested genes present were removed. Sewage-sludge biochar displayed interesting properties to minimize the spread of antimicrobial resistances to the aquatic environment while strengthening the role of WWTPs as resource recovery factories.Graphical abstractHighlightsSewage-sludge biochar and iron oxide coated sands were tested to adsorb DNA and cells.Biochar removed 97% of genes tested from environmental DNA of unfiltered effluent.85% of ARGs and MGEs of free-floating extracellular DNA were retained by biochar.Biochar is a WWTP by-product that can be re-used for public health sanitation.


Geoderma ◽  
2022 ◽  
Vol 411 ◽  
pp. 115698
Author(s):  
Xue-Mei Han ◽  
Hang-Wei Hu ◽  
Jin-Yang Li ◽  
He-Lian Li ◽  
Fang He ◽  
...  

2014 ◽  
Vol 80 (22) ◽  
pp. 6898-6907 ◽  
Author(s):  
Teddie O. Rahube ◽  
Romain Marti ◽  
Andrew Scott ◽  
Yuan-Ching Tien ◽  
Roger Murray ◽  
...  

ABSTRACTThe consumption of crops fertilized with human waste represents a potential route of exposure to antibiotic-resistant fecal bacteria. The present study evaluated the abundance of bacteria and antibiotic resistance genes by using both culture-dependent and molecular methods. Various vegetables (lettuce, carrots, radish, and tomatoes) were sown into field plots fertilized inorganically or with class B biosolids or untreated municipal sewage sludge and harvested when of marketable quality. Analysis of viable pathogenic bacteria or antibiotic-resistant coliform bacteria by plate counts did not reveal significant treatment effects of fertilization with class B biosolids or untreated sewage sludge on the vegetables. Numerous targeted genes associated with antibiotic resistance and mobile genetic elements were detected by PCR in soil and on vegetables at harvest from plots that received no organic amendment. However, in the season of application, vegetables harvested from plots treated with either material carried gene targets not detected in the absence of amendment. Several gene targets evaluated by using quantitative PCR (qPCR) were considerably more abundant on vegetables harvested from sewage sludge-treated plots than on vegetables from control plots in the season of application, whereas vegetables harvested the following year revealed no treatment effect. Overall, the results of the present study suggest that producing vegetable crops in ground fertilized with human waste without appropriate delay or pretreatment will result in an additional burden of antibiotic resistance genes on harvested crops. Managing human exposure to antibiotic resistance genes carried in human waste must be undertaken through judicious agricultural practice.


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