Degradation of extracellular genomic, plasmid DNA and specific antibiotic resistance genes by chlorination

Menglu Zhang , Sheng Chen , Xin Yu , Peter Vikesland , Amy Pruden

Front. Environ. Sci. Eng. ›› 2019, Vol. 13 ›› Issue (3) : 38

PDF (1008KB)
Front. Environ. Sci. Eng. ›› 2019, Vol. 13 ›› Issue (3) : 38 DOI: 10.1007/s11783-019-1124-5
RESEARCH ARTICLE
RESEARCH ARTICLE

Degradation of extracellular genomic, plasmid DNA and specific antibiotic resistance genes by chlorination

Author information +
History +
PDF (1008KB)

Abstract

Extracellular DNA structure damaged by chlorination was characterized.

Integrity of extracellular ARG genetic information after chlorination was determined.

Typical chlorine doses will likely effectively diminish extracellular DNA and ARGs.

Plasmid DNA/ARGs were less readily broken down than genomic DNA.

The Bioanalyzer methodology effectively documented damage incurred to DNA.

There is a need to improve understanding of the effect of chlorine disinfection on antibiotic resistance genes (ARGs) in order to advance relevant drinking water, wastewater, and reuse treatments. However, few studies have explicitly assessed the physical effects on the DNA. Here we examined the effects of free chlorine (1–20 mg Cl2/L) on extracellular genomic, plasmid DNA and select ARGs. Chlorination was found to decrease the fluorometric signal of extracellular genomic and plasmid DNA (ranging from 0.005 to 0.05 mg/mL) by 70%, relative to a no-chlorine control. Resulting DNA was further subject to a fragment analysis using a Bioanalyzer, indicating that chlorination resulted in fragmentation. Moreover, chlorine also effectively deactivated both chromosomal- and plasmid-borne ARGs, mecA and tetA, respectively. For concentrations >2 mg Cl2//L × 30 min, chlorine efficiently reduced the qPCR signal when the initial concentration of ARGs was 105 copies/mL or less. Notably, genomic DNA and mecA gene signals were more readily reduced by chlorine than the plasmid-borne tetA gene (by ~2 fold). Based on the results of qPCR with short (~200 bps) and long amplicons (~1200 bps), chlorination could destroy the integrity of ARGs, which likely reduces the possibility of natural transformation. Overall, our findings strongly illustrate that chlorination could be an effective method for inactivating extracellular chromosomal- and plasmid-borne DNA and ARGs.

Graphical abstract

Keywords

Antibiotic resistance / Antibiotic resistance genes (ARGs) / Extracellular DNA/ARGs / Chlorination

Cite this article

Download citation ▾
Menglu Zhang, Sheng Chen, Xin Yu, Peter Vikesland, Amy Pruden. Degradation of extracellular genomic, plasmid DNA and specific antibiotic resistance genes by chlorination. Front. Environ. Sci. Eng., 2019, 13(3): 38 DOI:10.1007/s11783-019-1124-5

登录浏览全文

4963

注册一个新账户 忘记密码

References

[1]

Bae J, Oh E, Jeon B (2014). Enhanced transmission of antibiotic resistance in Campylobacter jejuni biofilms by natural transformation. Antimicrobial Agents and Chemotherapy, 58(12): 7573–7575

[2]

Beebee T J (1991). Analysis, purification and quantification of extracellular DNA from aquatic environments. Freshwater Biology, 25(3): 525–532

[3]

Bellanger X, Guilloteau H, Bonot S, Merlin C (2014). Demonstrating plasmid-based horizontal gene transfer in complex environmental matrices: A practical approach for a critical review. Science of the Total Environment, 493: 872–882

[4]

Bergeron S, Boopathy R, Nathaniel R, Corbin A, LaFleur G (2015). Presence of antibiotic resistant bacteria and antibiotic resistance genes in raw source water and treated drinking water. International Biodeterioration & Biodegradation, 102: 370–374

[5]

Bertolla F, Simonet P (1999). Horizontal gene transfers in the environment: natural transformation as a putative process for gene transfers between transgenic plants and microorganisms. Research in Microbiology, 150(6): 375–384

[6]

Bichai F, Barbeau B, Dullemont Y, Hijnen W (2010). Role of predation by zooplankton in transport and fate of protozoan (oo)cysts in granular activated carbon filtration. Water Research, 44(4): 1072–1081

[7]

Blokesch M (2016). Natural competence for transformation. Current Biology, 26(21): R1126–R1130

[8]

Bukholm G, Tannaes T, Kjelsberg A B B, Smith-Erichsen N (2002). An outbreak of multidrug-resistant Pseudomonas aeruginosa associated with increased risk of patient death in an intensive care unit. Infection Control and Hospital Epidemiology, 23(08): 441–446

[9]

Burrows C J, Muller J G (1998). Oxidative nucleobase modifications leading to strand scission. Chemical Reviews, 98(3): 1109–1152

[10]

Chang P H, Juhrend B, Olson T M, Marrs C F, Wigginton K R (2017). Degradation of extracellular antibiotic resistance genes with UV254 treatment. Environmental Science & Technology, 51(11): 6185–6192

[11]

Clowes R C (1972). Molecular structure of bacterial plasmids. Bacteriological Reviews, 36(3): 361–405

[12]

Coniey E C, Saunders V A, Saunders J R (1986). Deletion and rearrangement of plasmid DNA during transformation of Escherichia coli with linear plasmid molecules. Nucleic Acids Research, 14(22): 8905–8917

[13]

Craun G F (2018). Waterborne Diseases in the US. Boca Raton, FL: CRC Press

[14]

Dalrymple O K, Stefanakos E, Trotz M A, Goswami D Y (2010). A review of the mechanisms and modeling of photocatalytic disinfection. Applied Catalysis B: Environmental, 98(1–2): 27–38

[15]

Davison J (1999). Genetic exchange between bacteria in the environment. Plasmid, 42(2): 73–91

[16]

de la Cruz F, Davies J (2000). Horizontal gene transfer and the origin of species: Lessons from bacteria. Trends in Microbiology, 8(3): 128–133

[17]

del Solar G, Giraldo R, Ruiz-Echevarría M J, Espinosa M, Díaz-Orejas R (1998). Replication and control of circular bacterial plasmids. Microbiology and Molecular Biology Reviews, 62(2): 434–464

[18]

Diep B A, Gill S R, Chang R F, Phan T H, Chen J H, Davidson M G, Lin F, Lin J, Carleton H A, Mongodin E F, Sensabaugh G F, Perdreau-Remington F (2006). Complete genome sequence of USA300, an epidemic clone of community-acquired meticillin-resistant Staphylococcus aureus. Lancet, 367(9512): 731–739

[19]

Dodd M C (2012). Potential impacts of disinfection processes on elimination and deactivation of antibiotic resistance genes during water and wastewater treatment. Journal of Environmental Monitoring, 14(7): 1754–1771

[20]

Dukan S, Touati D (1996). Hypochlorous acid stress in Escherichia coli: Resistance, DNA damage, and comparison with hydrogen peroxide stress. Journal of Bacteriology, 178(21): 6145–6150

[21]

Eischeid A C, Meyer J N, Linden K G (2009). UV disinfection of adenoviruses: Molecular indications of DNA damage efficiency. Applied and Environmental Microbiology, 75(1): 23–28

[22]

Fernando D M, Tun H M, Poole J, Patidar R, Li R, Mi R, Amarawansha G E A, Fernando W G D, Khafipour E, Farenhorst A, Kumar A (2016). Detection of antibiotic resistance genes in source and drinking water samples from a First Nations Community in Canada. Applied and Environmental Microbiology, 82(15): 4767–4775

[23]

Fleige S, Pfaffl M W (2006). RNA integrity and the effect on the real-time qRT-PCR performance. Molecular Aspects of Medicine, 27(2–3): 126–139

[24]

Freeman C N, Scriver L, Neudorf K D, Truelstrup Hansen L, Jamieson R C, Yost C K (2018). Antimicrobial resistance gene surveillance in the receiving waters of an upgraded wastewater treatment plant. FACETS, 3(1): 128–138

[25]

Fricke W F, Wright M S, Lindell A H, Harkins D M, Baker-Austin C, Ravel J, Stepanauskas R (2008). Insights into the environmental resistance gene pool from the genome sequence of the multidrug-resistant environmental isolate Escherichia coli SMS-3-5. Journal of Bacteriology, 190(20): 6779–6794

[26]

Frischer M E, Stewart G J, Paul J H (1994). Plasmid transfer to indigenous marine bacterial populations by natural transformation. FEMS Microbiology Ecology, 15(1–2): 127–135

[27]

Harrison E, Brockhurst M A (2012). Plasmid-mediated horizontal gene transfer is a coevolutionary process. Trends in Microbiology, 20(6): 262–267

[28]

Hawkins C L, Davies M J (2002). Hypochlorite-induced damage to DNA, RNA, and polynucleotides: Formation of chloramines and nitrogen-centered radicals. Chemical Research in Toxicology, 15(1): 83–92

[29]

Howe K J, Crittenden J C, Hand D W, Trussell R R, Tchobanoglous G (2012). Principles of Water Treatment. Hoboken, NJ: John Wiley & Sons

[30]

Huang J J, Hu H Y, Wu Y H, Wei B, Lu Y (2013). Effect of chlorination and ultraviolet disinfection on tetA-mediated tetracycline resistance of Escherichia coli. Chemosphere, 90(8): 2247–2253

[31]

Jia S, Shi P, Hu Q, Li B, Zhang T, Zhang X X (2015). Bacterial community shift drives antibiotic resistance promotion during drinking water chlorination. Environmental Science & Technology, 49(20): 12271–12279

[32]

Jiang L, Hu X, Xu T, Zhang H, Sheng D, Yin D (2013). Prevalence of antibiotic resistance genes and their relationship with antibiotics in the Huangpu River and the drinking water sources, Shanghai, China. Science of the Total Environment, 458 460: 267–272

[33]

Jiang X, Ellabaan M M H, Charusanti P, Munck C, Blin K, Tong Y, Weber T, Sommer M O A, Lee S Y (2017). Dissemination of antibiotic resistance genes from antibiotic producers to pathogens. Nature Communications, 8: 15784

[34]

Kulkarni P, Olson N D, Paulson J N, Pop M, Maddox C, Claye E, Rosenberg Goldstein R E, Sharma M, Gibbs S G, Mongodin E F, Sapkota A R (2018). Conventional wastewater treatment and reuse site practices modify bacterial community structure but do not eliminate some opportunistic pathogens in reclaimed water. Science of the Total Environment, 639: 1126–1137

[35]

Lau H Y, Ashbolt N J (2009). The role of biofilms and protozoa in Legionella pathogenesis: Implications for drinking water. Journal of Applied Microbiology, 107(2): 368–378

[36]

Lerman L S, Tolmach L J (1959). Genetic transformation. II. The significance of damage to the DNA molecule. Biochimica et Biophysica Acta, 33(2): 371–387

[37]

Li Y H, Lau P C, Lee J H, Ellen R P, Cvitkovitch D G (2001). Natural genetic transformation of Streptococcus mutans growing in biofilms. Journal of Bacteriology, 183(3): 897–908

[38]

Liu Q, Li M, Liu X, Zhang Q, Liu R, Wang Z, Shi X, Quan J, Shen X, Zhang F (2018a). Removal of sulfamethoxazole and trimethoprim from reclaimed water and the biodegradation mechanism. Frontiers of Environmental Science & Engineering, 12(6): 6

[39]

Liu S S, Qu H M, Yang D, Hu H, Liu W L, Qiu Z G, Hou A M, Guo J, Li J W, Shen Z Q, Jin M (2018b). Chlorine disinfection increases both intracellular and extracellular antibiotic resistance genes in a full-scale wastewater treatment plant. Water Research, 136: 131–136

[40]

Lorenz M G, Wackernagel W (1994). Bacterial gene transfer by natural genetic transformation in the environment. Microbiological Reviews, 58(3): 563–602

[41]

Masotti A, Preckel T (2006). Analysis of small RNAs with the Agilent 2100 Bioanalyzer. Nature Methods, 3(8): 658

[42]

McKinney C W, Loftin K A, Meyer M T, Davis J G, Pruden A (2010). tet and sul antibiotic resistance genes in livestock lagoons of various operation type, configuration, and antibiotic occurrence. Environmental Science & Technology, 44(16): 6102–6109

[43]

McKinney C W, Pruden A (2012). Ultraviolet disinfection of antibiotic resistant bacteria and their antibiotic resistance genes in water and wastewater. Environmental Science & Technology, 46(24): 13393–13400

[44]

Metch J W, Ma Y, Pruden A, Vikesland P J (2015). Enhanced disinfection by-product formation due to nanoparticles in wastewater treatment plant effluents. Environmental Science. Water Research & Technology, 1(6): 823–831

[45]

Öncü N B, Menceloğlu Y Z, Balcıoğlu I A (2011). Comparison of the effectiveness of chlorine, ozone, and photocatalytic disinfection in reducing the risk of antibiotic resistance pollution. Journal of Advanced Oxidation Technologies, 14(2): 196–203

[46]

Park J, Park W (2011). Phenotypic and physiological changes in Acinetobacter sp. strain DR1 with exogenous plasmid. Current Microbiology, 62(1): 249–254

[47]

Pecson B M, Ackermann M, Kohn T (2011). Framework for using quantitative PCR as a nonculture based method to estimate virus infectivity. Environmental Science & Technology, 45(6): 2257–2263

[48]

Pinto A J, Xi C, Raskin L (2012). Bacterial community structure in the drinking water microbiome is governed by filtration processes. Environmental Science & Technology, 46(16): 8851–8859

[49]

Prütz W A (1996). Hypochlorous acid interactions with thiols, nucleotides, DNA, and other biological substrates. Archives of Biochemistry and Biophysics, 332(1): 110–120

[50]

Prütz W A (1998). Interactions of hypochlorous acid with pyrimidine nucleotides, and secondary reactions of chlorinated pyrimidines with GSH, NADH, and other substrates. Archives of Biochemistry and Biophysics, 349(1): 183–191

[51]

Sanganyado E, Gwenzi W (2019). Antibiotic resistance in drinking water systems: Occurrence, removal, and human health risks. Science of the Total Environment, 669: 785–797

[52]

Shah A D, Liu Z Q, Salhi E, Höfer T, Werschkun B, Von Gunten U (2015). Formation of disinfection by-products during ballast water treatment with ozone, chlorine, and peracetic acid: Influence of water quality parameters. Environmental Science. Water Research & Technology, 1(4): 465–480

[53]

Sinha S, Redfield R J (2012). Natural DNA uptake by Escherichia coli. PLoS One, 7(4): e35620

[54]

Srinivasan A, Lehmler H J, Robertson L W, Ludewig G (2001). Production of DNA strand breaks in vitro and reactive oxygen species in vitro and in HL-60 cells by PCB metabolites. Toxicological Sciences, 60(1): 92–102

[55]

Su H C, Liu Y S, Pan C G, Chen J, He L Y, Ying G G (2018). Persistence of antibiotic resistance genes and bacterial community changes in drinking water treatment system: From drinking water source to tap water. Science of the Total Environment, 616 617: 453–461

[56]

Suquet C, Warren J J, Seth N, Hurst J K (2010). Comparative study of HOCl-inflicted damage to bacterial DNA ex vivo and within cells. Archives of Biochemistry and Biophysics, 493(2): 135–142

[57]

Thomas C M, Nielsen K M (2005). Mechanisms of, and barriers to, horizontal gene transfer between bacteria. Nature Reviews. Microbiology, 3(9): 711–721

[58]

Thomas J M, Ashbolt N J (2011). Do free-living amoebae in treated drinking water systems present an emerging health risk? Environmental Science & Technology, 45(3): 860–869

[59]

Tornevi A, Simonsson M, Forsberg B, Säve-Söderbergh M, Toljander J (2016). Efficacy of water treatment processes and endemic gastrointestinal illness: A multi-city study in Sweden. Water Research, 102: 263–270

[60]

Volkmann H, Schwartz T, Kirchen S, Stofer C, Obst U (2007). Evaluation of inhibition and cross-reaction effects on real-time PCR applied to the total DNA of wastewater samples for the quantification of bacterial antibiotic resistance genes and taxon-specific targets. Molecular and Cellular Probes, 21(2): 125–133

[61]

Wen G, Xu X, Huang T, Zhu H, Ma J (2017). Inactivation of three genera of dominant fungal spores in groundwater using chlorine dioxide: Effectiveness, influencing factors, and mechanisms. Water Research, 125: 132–140

[62]

Xu L, Ouyang W, Qian Y, Su C, Su J, Chen H (2016). High-throughput profiling of antibiotic resistance genes in drinking water treatment plants and distribution systems. Environmental Pollution, 213: 119–126

[63]

Xu L, Zhang C, Xu P, Wang X C (2017). Mechanisms of ultraviolet disinfection and chlorination of Escherichia coli: Culturability, membrane permeability, metabolism, and genetic damage. Journal of Environmental Sciences-China, 65: 356–366

[64]

Yoon Y, Dodd M C, Lee Y (2018). Elimination of transforming activity and gene degradation during UV and UV/H2O2 treatment of plasmid-encoded antibiotic resistance genes. Environmental Science: Water Research & Technology, 4(9): 1239–1251

[65]

Yuan Q B, Guo M T, Yang J (2015). Fate of antibiotic resistant bacteria and genes during wastewater chlorination: Implication for antibiotic resistance control. PLoS One, 10(3): e0119403

[66]

Zhang T, Hu Y, Jiang L, Yao S, Lin K, Zhou Y, Cui C (2019). Removal of antibiotic resistance genes and control of horizontal transfer risk by UV, chlorination and UV/chlorination treatments of drinking water. Chemical Engineering Journal, 358: 589–597

[67]

Zhang X, Wu B, Zhang Y, Zhang T, Yang L, Fang H H P, Ford T, Cheng S (2009a). Class 1 integronase gene and tetracycline resistance genes tetA and tetC in different water environments of Jiangsu Province, China. Ecotoxicology (London, England), 18(6): 652–660

[68]

Zhang X, Zhang T, Fang H H(2009b). Antibiotic resistance genes in water environment. Applied Microbiology and Biotechnology, 82(3): 397–414

RIGHTS & PERMISSIONS

Higher Education Press and Springer-Verlag GmbH Germany, part of Springer Nature

AI Summary AI Mindmap
PDF (1008KB)

3782

Accesses

0

Citation

Detail

Sections
Recommended

AI思维导图

/