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      Antibiotic resistance is the quintessential One Health issue

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          Abstract

          The scale of antimicrobial resistance In May this year, the long-awaited final report from the Review on Antimicrobial Resistance was published. 1 The report estimates that the 700 000 annual deaths currently attributable to infections by drug-resistant pathogens will increase, if unchecked, to 10 million by 2050, running up a bill of US$100 trillion in terms of lost global production between now and then. The reported numbers are somewhat apocalyptic, as they are based on crude projections of current trends and presume the failure of anti-malarial drugs and antiretroviral therapy as well as antibiotics. Nor do they account for the possible entry of new drugs onto the market. There is huge uncertainty associated with the human burden of antimicrobial resistance (AMR) in general and antibiotic resistance in particular (for the purpose of this article the widely used term antimicrobial resistance [AMR] is retained, though the emphasis here is on antibiotic resistance). The precision of the estimates does not really matter much: the point is that the problem is already immense and is growing rapidly. We have been squandering our antibiotic resources for far too long and immediate action is needed on a very large scale if we are to reverse current trends. AMR as a One Health issue It is difficult to imagine an issue that epitomises the principles of One Health more than AMR does. The One Health approach, defined as ‘...the collaborative effort of multiple disciplines – working locally, nationally, and globally – to attain optimal health for people, animals and our environment…’, 2 recognises that the health of people is connected to the health of animals and the environment. AMR has clear links to each of these three domains. The contribution of animal production, both terrestrial livestock and aquaculture, to the global AMR crises is questioned by some on the grounds that we don't see so many animal-associated infections in humans. 3 While this may be true, because of the way that many antibiotics are used in animal production, in sub-therapeutic doses and with long exposure periods, these production systems create ideal conditions for bacteria to fix genes that confer resistance. These genes can subsequently be transmitted to human-adapted pathogens or to human gut microbiota via people, contaminated food or the environment. They also provide ideal conditions for the amplification of genes that may have arisen in people or the environment. The fact that the antibiotics used in human and animal health largely comprise the same or very similar molecules would be expected to drive the transmission of resistance between animals and people, either directly or via the environment. Of the three domains, human health takes the spotlight, with multidrug-resistance genes now highly prevalent in many important and common pathogens like Escherichia coli, Klebsiella pneumoniae and Staphylococcus aureus. Quite apart from the many infectious diseases for which we rely on antibiotics to combat, these drugs underpin modern medicine by allowing us to carry out common surgical procedures and treatments that depress the immune system, such as chemotherapy to treat cancer. The global burden of AMR on the population has been estimated, 1,4 and more specific studies have also been carried out; for example, the estimated 214 000 neonatal deaths attributable to resistant sepsis infections globally in 2013; 111 523 occurring in the five countries with the highest numbers of neonatal deaths in the world: India, Pakistan, Nigeria, Democratic Republic of Congo and China. 5 Such estimates of the burden of AMR have not been attempted for livestock or aquaculture, perhaps due to a perceived lower importance. Resistance to antibiotics among mastitis pathogens, for example, is well documented though it is not considered to be an emerging or a progressing problem. 6 Recent estimates of the amount of antibiotics consumed in livestock production conservatively place this at 63 151 tonnes in 2010. 7 The situation is less clear in aquaculture. 8 Although actual figures are currently unavailable, the published estimates of the proportion of antibiotics consumed in animal agriculture—84% (for 36 antibiotics) in China 9 and 70% in USA 10 —suggest global agricultural consumption probably exceeds that of humans. A large part of this use is justified and valid on veterinary grounds, 6 but there is much misuse in the agricultural sector. With such large consumption levels it seems likely that agricultural use contributes significantly to AMR. A recent review suggested that misuse of antimicrobials in animal production is a clear and substantial driver of AMR, 11 and there is a growing body of evidence linking antibiotic consumption in livestock to AMR in the clinic. 12 Many infections in people are endogenous; derived from the human gut flora. An important gap in knowledge relates to the possible extent and mechanisms of transmission of antibiotic resistance genes between the normal gut flora of animals and that of humans. The third One Health pillar, environmental health, including that of crops where antimicrobials are also used in plant protection, 13 is the least well understood in this tangled web of antibiotic gene evolution, transmission and persistence. Environmental bacteria, being quantitatively the most prevalent organisms, serve as sources for AMR genes that can become incorporated, over time, into pathogens of people and animals. This naturally occurring phenomenon is exacerbated by the influx to the environment of AMR genes from livestock and human waste 14 and by the vast quantities of antibiotic residues that enter the environment from the pharmaceutical industry, 15 from intensive livestock farms 16 and from hospitals. 17 Because of this, it has been proposed that these activities represent effective hotspots for the development and spread of AMR genes. 18 The impact of such factors is likely to be more pronounced in developing countries with lax environmental legislation and enforcement. Soil and water microflora play complex and critical roles in ecosystem functions such as the recycling of carbon and nutrients. Disrupting these vital processes by creating an imbalance may threaten planetary health, 19 potentially pushing ecosystems beyond critical environmental thresholds. 20 The relative roles of these three domains in the development, transmission and persistence of AMR genes is poorly understood. A truly One Health approach to dealing with AMR, embracing all three domains, will depend on a sound grasp of the relative importance of each in the evolution of AMR bacteria and genetic determinants, the ways in which they interact, and the transmission routes and mechanisms involved. AMR is also a One World issue As well as being a One Health issue, AMR is a One World issue. The globalisation of the food system, with increasing movement of livestock and agricultural produce, combined with increasing human travel, facilitates the rapid spread and mixing of AMR genes that emerge. A worrying example is the emergence of a plasmid-mediated resistance gene (mcr-1) to colistin, a last-resort antibiotic, identified in people and pigs in China last year. 21 This was followed by its rapid spread across Europe and Canada to the USA, where it has recently been identified. 22 A similar case is the spread of New Delhi metallobeta-lactamase 1 (NDM-1), a transmissible genetic element encoding resistance genes against most known beta-lactam antibiotics, from its point of emergence in New Delhi, India, in 2008. 23 Likened in this regard to carbon emissions, 24 no matter how good a country's programme of antimicrobial stewardship in health and agriculture, they are laid bare to the importation of AMR genes that have emerged and spread from other parts of the world. Such rapid spread of resistance must surely create a disincentive for the pharmaceutical industry, with an eye on profits from high income countries (HICs), to develop new antimicrobials against which AMR genes may be rapidly acquired through abuse in low- and middle-income countries (LMICs). The other factor making AMR a One World issue is that dealing with AMR is central to the long-term economic development of countries and to our global well-being. 1 LMICs face the greatest burden of AMR because of their disease-prone environments, poorer sanitary standards and, for the poorest, much reduced access to effective antibiotics. 5 Poor access to competent veterinary and extension services leaves farmers in LMICs with antibiotics as their only resource to tackle endemic bacterial animal infections. Interventions must be based on an understanding of and respect for the different social and socio-economic contexts in which they are to be implemented. AMR is a global problem calling for global solutions: but the solutions will not be the same in every country, or among different socio-economic groups. Some use antimicrobials too much, some too little and many use them unwisely: understanding patterns of use and incentives for changing these, and exploring alternative options, must underpin any reduction efforts. Increasing recognition of AMR The Review on Antimicrobial Resistance comes at an important time and has no-doubt already been influential in bringing this critical topic into the arena of global public debate among stakeholders who would normally have not paid attention to this problem. The commitment by G7 countries in Berlin in 2015, to promote the AMR agenda, was cemented at this year's G7 Ise-Shima Summit in Japan, at which it was proposed to ‘promote the One Health Approach to tackle cross-cutting issues of AMR in human and animal health, agriculture food and the environment, and take actions involving multiple sectors, such as by integrating collaboration between the responsible ministries, in line with the 2015 WHO Global Action Plan on AMR adopted and relevant resolutions of FAO and OIE.’ 25 In May 2015, the 68th World Health Assembly endorsed a resolution making it mandatory for member countries to align national action plans with the global standard by May 2017, and WHO subsequently published the Global Action Plan on Antimicrobial Resistance 26 to guide Member States in developing their plans. It is expected that a resolution will be adopted at the 71st Session of the United Nations General Assembly in September 2016, which, if effective, could place national governments under pressure to take action towards reducing consumption of antibiotics in both human medicine and agriculture. Call for interdisciplinary research in support of appropriate action Whatever action we take will only be sustainable if it is based on a sound understanding of the relative roles of people, animals and the environment in the emergence, spread and persistence of AMR genes. This is not a problem that HICs will be able to solve alone. The important role that animal agriculture plays in livelihoods in LMICs is unknown or underestimated by many in HICs and needs to be an integral part of the thinking and negotiation if we want to avoid the pitfalls seen in climate negotiations, with LMICs often reluctant to take measures that may compromise their short-term economic development. The One Health science seems to fall short when it comes to understanding the economic forces behind many emerging infectious diseases; there is a further gap to be bridged between the biomedical, environmental and animal sciences, and the social sciences. Integrated approaches to reduce selection pressure and disrupt AMR transmission cycles on a global scale must be sought that are founded not only on sound One Health principles, but also based on economic evidence and on principles of social equity and global access to effective healthcare for people and their animals.

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          Most cited references13

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          Effluent from drug manufactures contains extremely high levels of pharmaceuticals.

          It is generally accepted that the main route for human pharmaceuticals to the aquatic environment is via sewage treatment plants receiving wastewater from households and hospitals. We have analysed pharmaceuticals in the effluent from a wastewater treatment plant serving about 90 bulk drug manufacturers in Patancheru, near Hyderabad, India--a major production site of generic drugs for the world market. The samples contained by far the highest levels of pharmaceuticals reported in any effluent. The high levels of several broad-spectrum antibiotics raise concerns about resistance development. The concentration of the most abundant drug, ciprofloxacin (up to 31,000 microg/L) exceeds levels toxic to some bacteria by over 1000-fold. The results from the present study call for an increased focus on the potential release of active pharmaceutical ingredients from production facilities in different regions.
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            Antibiotic resistance gene abundances associated with antibiotics and heavy metals in animal manures and agricultural soils adjacent to feedlots in Shanghai; China.

            Eight antibiotic resistance genes (ARGs), 7 heavy metals, and 6 antibiotics were quantified in manures and soils collected from multiple feedlots in Shanghai. The samples were analyzed to determine if ARG abundances were associated with heavy metal concentration and independent of antibiotics. The results revealed the presence of chloramphenicol, sulfonamides and tetracyclines at concentration ranges of 3.27-17.85, 5.85-33.37 and 4.54-24.66 mg kg(-1), respectively. Typical heavy metals, such as Cu, Zn, and As, were detected at concentration ranges of 32.3-730.1, 75.9-4333.8, and 2.6-617.2 mg kg(-1). All ARGs tested were detected in the collected samples except tetB(P), which was absent in animal manures. Overall, sulfonamide ARGs were more abundant than tetracycline ARGs. Except for sulII, only a weak positive correlation was found between ARGs and their corresponding antibiotics. On the contrary, significant positive correlations (p<0.05) were found between some ARGs and typical heavy metals. For example, sulA and sulIII were strongly correlated with levels of Cu, Zn and Hg. The data demonstrated that the presence of ARGs was relatively independent of their respective antibiotic inducer. In addition to antibiotics, toxic heavy metals, such as Hg, Cu, and Zn, exerted a strong selection pressure and acted as complementary factors for ARG abundance. Copyright © 2012 Elsevier B.V. All rights reserved.
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              Escherichia coli Harboring mcr-1 and blaCTX-M on a Novel IncF Plasmid: First Report of mcr-1 in the United States

              LETTER The recent discovery of a plasmid-borne colistin resistance gene, mcr-1, in China heralds the emergence of truly pan-drug-resistant bacteria (1). The gene has been found primarily in Escherichia coli but has also been identified in other members of the Enterobacteriaceae in human, animal, food, and environmental samples on every continent (2 – 5). In response to this threat, starting in May 2016, all extended-spectrum-β-lactamase (ESBL)-producing E. coli clinical isolates submitted to the clinical microbiology laboratory at the Walter Reed National Military Medical Center (WRNMMC) have been tested for resistance to colistin by Etest. Here we report the presence of mcr-1 in an E. coli strain cultured from a patient with a urinary tract infection (UTI) in the United States. The strain was resistant to colistin, but it remained susceptible to several other agents, including amikacin, piperacillin-tazobactam, all carbapenems, and nitrofurantoin (Table 1). E. coli MRSN 388634 was cultured from the urine of a 49-year-old female who presented to a clinic in Pennsylvania on 26 April 2016 with symptoms indicative of a UTI. The isolate was forwarded to WRNMMC, where susceptibility testing indicated an ESBL phenotype (Table 1). The isolate was included in the first 6 ESBL-producing E. coli isolates selected for colistin susceptibility testing, and it was the only isolate to have a MIC of colistin of 4 μg/ml (all of the others had MICs of ≤0.25 μ/ml). The colistin MIC was confirmed by broth microdilution, and mcr-1 was detected by real-time PCR (6). Whole-genome sequencing (WGS) of MRSN 388634 was performed using a PacBio RS II system and a MiSeq benchtop sequencer. TABLE 1 Antibiotic resistance profile of MRSN 388634 Antibiotic(s) MIC(s) (μg/ml) a Amikacin ≤8, S Amoxicillin/clavulanate 16/8, I Ampicillin >16, R Aztreonam >16, R Cefazolin >16, R Cefepime >16, R Ceftazidime >16, R Ceftriaxone >32, R Ciprofloxacin >2, R Colistin 4, R Ertapenem ≤0.25, S Gentamicin >8, R Imipenem ≤0.25, S Levofloxacin >4, R Meropenem ≤0.25, S Nitrofurantoin ≤16, S Piperacillin-tazobactam 4/4, S Tetracycline >8, R Tobramycin >8, R Trimethoprim-sulfamethoxazole >2/38, R a MICs were determined using BD Phoenix (BD Diagnostics Systems, Hunt Valley, MD, USA) with panels NMIC/ID 133, except for colistin, for which determinations were performed using Etest and manual broth microdilution; both gave MICs of colistin of 4 μg/ml. R = resistant, I = intermediate, and S = susceptible, based on CLSI guidelines (except for colistin, where EUCAST breakpoints are used). E. coli MRSN 388634 belonged to sequence type 457 (ST457), a rare E. coli ST first identified in 2008 from a urine culture in the United Kingdom (7). It was subsequently identified from a bloodstream culture in Italy, where it was found to harbor the carbapenemase genes bla KPC-3 and bla CTX-M-55 (8). MRSN 388634 carried 15 antibiotic resistance genes, which were harbored on two plasmids, but no carbapenemases (Table 2). TABLE 2 Characteristics of plasmids in E. coli MRSN 388634 Plasmid name Size (kb) Inc a Copy no. b Antibiotic resistance genes c pMR0516mcr 225.7 F18:A-:B1 2 strA, strB, bla CTX-M-55, bla TEM-1B, mcr-1 , sul2, tet(A), dfrA14 pMR0416ctx 47 N 1 aac(3)-IVa, aph(4)-Ia, bla CTX-M-14, fosA3, mph(A), floR, sul2 a Data represent plasmid incompatibility (Inc) group designations, as determined by Plasmid Finder version 1.2 (10). b Data represent average numbers of copies per cell, normalized to the chromosomal read coverage. c The gene of interest is indicated in bold. The first plasmid, pMR0516mcr, was 225,707 bp in size and belonged to incompatibility group F18:A-:B1 (9). BLAST analysis indicated that pMR0516mcr represented a novel IncF plasmid. Notably, it shares 89 kb of homologous sequence with pHNSHP45-2, a mcr-1-carrying IncHI2 plasmid described by Liu and colleagues (1). This shared sequence contains mcr-1 in association with ISApl1 (1), but in pMR0516mcr it is in a different location and orientation (Fig. 1). pMR0516mcr also carried 7 additional antibiotic resistance genes, including the ESBL gene bla CTX-M-55 (Table 2). The second plasmid, pMR0416ctx, was ∼47 kb in size and was assigned to IncN (Table 2). It carried 7 antibiotic resistance genes, including bla CTX-M-14. A complete description of both plasmids is under preparation. FIG 1 Comparison of the homologous regions containing mcr-1 shared by pMR0516mcr and pHNSHP45-2. Open arrows represent coding sequences (green arrows, mcr-1; white arrows, ISapl1; purple arrows, metabolic function; blue arrows, plasmid replication and maintenance; gray arrows, hypothetical and unclassified) and indicate direction of transcription. The arrow size is proportional to the gene length. The gray and blue areas between pMR0516mcr and pHNSHP45-2 indicate nucleotide identity of >99.9% by BLASTN. To the best of our knowledge, this is the first report of mcr-1 in the United States. The epidemiology of MRSN 388634 is noteworthy; the isolate was submitted from a clinic in Pennsylvania, and the patient reported no travel history within the prior 5 months. To date, a further 20 ESBL-producing E. coli isolates from patients at the WRNMMC have tested negative for mcr-1 and have been colistin sensitive. However, as testing has been ongoing for only 3 weeks, it remains unclear what the true prevalence of mcr-1 is in the population. The association between mcr-1 and IncF plasmids is concerning, as these plasmids are vehicles for the dissemination of antibiotic resistance and virulence genes among the Enterobacteriaceae (9). Continued surveillance to determine the true frequency for this gene in the United States is critical. Nucleotide sequence accession numbers. The Short Read Archive (SRA) file for MRSN 388623 has been deposited at GenBank with accession number SRP075674. The complete sequence of pMR0516mcr has been deposited at GenBank with accession no. KX276657.
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                Author and article information

                Journal
                Trans R Soc Trop Med Hyg
                Trans. R. Soc. Trop. Med. Hyg
                trstmh
                trstmh
                Transactions of the Royal Society of Tropical Medicine and Hygiene
                Oxford University Press
                0035-9203
                1878-3503
                July 2016
                05 August 2016
                05 August 2016
                : 110
                : 7
                : 377-380
                Affiliations
                [a ]International Livestock Research Institute, Nairobi, Kenya
                [b ]Institute of Animal Science, Chinese Academy of Agricultural Sciences, Beijing, China
                [c ]Oxford University Clinical Research Unit, Wellcome Trust Major Overseas Programme, Ho Chi Minh City, Vietnam
                [d ]Institute of Infection and Global Health, University of Liverpool, Liverpool, UK
                [e ]Université Libre de Bruxelles, Brussels, Belgium
                [f ]Institute for Health Metrics and Evaluation, University of Washington , Seattle, USA
                [g ]Oxford Big Data Institute, Li Ka Shing Centre for Health Information and Discovery, Oxford, UK
                [h ]Research Group for Preventive Technology in Livestock, Faculty of Veterinary Medicine, Khon Kaen University, Khon Kaen, Thailand
                [i ]Public Health Foundation of India, Delhi, India
                [j ]Kenya Medical Research Institute, Nairobi, Kenya
                [k ]Center for Disease Dynamics, Economics and Policy, Washington DC, USA
                [l ]Food and Agriculture Organization of the United Nations, Rome, Italy
                [m ]Department of Clinical Sciences, Swedish University of Agricultural Sciences, Uppsala, Sweden
                [n ]National Institute of Veterinary Research, Hanoi, Vietnam
                [o ]Institute of Integrative Biology and Center for Adaptation to a Changing Environment, Swiss Federal Institute of Technology, Zurich, Switzerland
                [p ]Centre for Immunity, Infection & Evolution, University of Edinburgh, Edinburgh, UK
                Author notes
                [* ]Corresponding author: Tel: +254 20 422 3020; E-mail: t.robinson@ 123456cgiar.org
                Article
                trw048
                10.1093/trstmh/trw048
                4975175
                27475987
                3bf03e44-d8f3-42c6-b019-2d869e9208fc
                © The Author 2016. Published by Oxford University Press on behalf of Royal Society of Tropical Medicine and Hygiene.

                This is an Open Access article distributed under the terms of the Creative Commons Attribution Non-Commercial License ( http://creativecommons.org/licenses/by-nc/4.0/), which permits non-commercial re-use, distribution, and reproduction in any medium, provided the original work is properly cited. For commercial re-use, please contact journals.permissions@oup.com

                History
                : 20 June 2016
                : 28 June 2016
                : 30 June 2016
                Funding
                Funded by: Agriculture for Nutrition and Health;
                Funded by: Medical Research Council; Natural Environment Research Council; Economic and Social Research Council; and the Biotechnology and Biosciences Research Council;
                Award ID: G1100783/1
                Funded by: Bill & Melinda Gates Foundation;
                Award ID: OPP1119467
                Award ID: OPP1093011
                Award ID: OPP1106023
                Award ID: OPP1132415
                Categories
                Editorial

                Medicine
                antibiotics,antimicrobial resistance (amr),environment,health,livestock,one health
                Medicine
                antibiotics, antimicrobial resistance (amr), environment, health, livestock, one health

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