2019
DOI: 10.1016/j.watres.2019.114906
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Antibiotic resistance and class 1 integron gene dynamics along effluent, reclaimed wastewater irrigated soil, crop continua: elucidating potential risks and ecological constraints

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Cited by 62 publications
(39 citation statements)
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“…Wastewater-irrigated soil in lysimeters had higher relative and absolute abundance of intl1 genes compared to freshwater-irrigated lysimeters. However, almost all ARGs were below detection limits in all tested soils, even after irrigation with treated wastewater [ 42 ]. A third study in Israel compared soils irrigated with greywater treated by constructed wetlands to soils irrigated with freshwater, with no difference in the abundance of tetracycline-resistant bacteria between the two types of soils [ 43 ].…”
Section: Resultsmentioning
confidence: 99%
“…Wastewater-irrigated soil in lysimeters had higher relative and absolute abundance of intl1 genes compared to freshwater-irrigated lysimeters. However, almost all ARGs were below detection limits in all tested soils, even after irrigation with treated wastewater [ 42 ]. A third study in Israel compared soils irrigated with greywater treated by constructed wetlands to soils irrigated with freshwater, with no difference in the abundance of tetracycline-resistant bacteria between the two types of soils [ 43 ].…”
Section: Resultsmentioning
confidence: 99%
“…In the absence of sufficient data and adequate methods to support a robust risk assessment focused on antibiotic resistance, it is valuable to identify approaches that can be used to establish a baseline level of risk in the interim. (Garner et al, 2018(Garner et al, , 2019Harb et al, 2019;Marano et al, 2019;Kampouris et al, 2021), which has been proposed as a monitoring target for antibiotic resistance given the ability of this integron to carry multiple ARGs and its propensity for horizontal gene transfer (Berendonk et al, 2015;Gillings et al, 2015). Others used metagenomic sequencing to identify ARGs associated mobile genetic elements, such as plasmids (Garner et al, 2018) In addition to the need to ensure that reported ARB and ARG data in recycled water can inform efforts at risk assessment, there are several key research gaps that remain in how to apply traditional QMRA approaches to antibiotic resistant pathogens.…”
Section: Integration Of Monitoring Results Into Risk Assessment Frameworkmentioning
confidence: 99%
“…Studies evaluating the prevalence of AMR in WWTP effluent indicate that wastewater treatment processes, including some secondary and tertiary treatment and disinfection processes, may not fully eliminate AMR bacteria and ARGs and that surviving bacteria retain their resistance properties [41,72,97,113,115,[122][123][124][125][126][127][128][129]. Hiller et al [72] reviewed the available literature on the levels of AMR bacteria and ARGs present following treatment with common WWTP processes, including disinfection with UV, ozone, and chlorine, to assess their efficacy.…”
Section: Treated Wastewatermentioning
confidence: 99%
“…Hiller et al [72] concluded "these findings confirm that discharge from WWTPs can result in significant contributions of AMR to the aquatic environment." Treatment processes commonly used at WWTPs are not typically calibrated to target removal of AMR bacteria or ARGs, with concerns about persistence and transformation of both cell-associated ARGs and extracellular DNA coding for antibiotic resistance [127,128]. The effectiveness of some disinfectants, including chlorine and ozone, are impacted by dose, contact time, temperature, and water quality variables (e.g., pH, turbidity, presence of ammonia and oxidant demand) [130,131].…”
Section: Treated Wastewatermentioning
confidence: 99%