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      A planetary vision for one health

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          Planetary Health, EcoHealth and One Health In 2015, the Rockefeller Foundation-Lancet Commission published a report: Safeguarding Human Health in the Anthropocene Epoch.1 This report outlines the extent to which human activities have degraded the earth’s ecosystems such that basic life support services have become threatened. Among the threats are greenhouse gases and resulting climate change, severe weather patterns, deforestation, desertification, ocean acidification, zoonotic disease outbreaks, biodiversity loss and particulate air pollution. The report concludes that these planetary phenomena pose a serious and urgent threat to human health, well-being and sustainability, and calls for immediate attention to critical multidisciplinary research, and evidence-based policy formulation and timely implementation. The Lancet Commission report has spawned a number of Planetary Health efforts, focused on policy, education and research, with initial support provided by the Rockefeller Foundation and more recently the Wellcome Trust.2 Activities include formation of a Planetary Health Alliance of over 95 universities, non-governmental organisations, government entities, research institutes and other partners, a website portal,3 an annual Planetary Health conference, and a new journal dedicated to the topic.4 Interest in the Planetary Health approach has led to a re-examination of similar existing approaches such as One Health5 and EcoHealth.6 One Health, an interdisciplinary approach stressing connections between human, animal and environmental health, gained momentum as a response to the steadily increasing drumbeat of emerging zoonotic disease outbreaks in recent decades, including the West Nile virus, severe acute respiratory syndrome, Nipah and Hendra viruses, Ebola, avian influenza, H1N1 2009 pandemic influenza,5 and most recently Ebola in West Africa, zika and yellow fever.7 The threat to global health from antimicrobial resistance, now understood to stem from overuse of antibiotics in both humans and animals, with environmental accumulation of antibiotic residues and resistant organisms and genes, has led to further support for One Health solutions.8 A recent editorial in The BMJ highlighted the utility of a One Health approach.9 The One Health approach has now been endorsed by numerous international agencies, including the WHO, the United Nations Food and Agriculture Organisation and the World Organisation for Animal Health (OIE),10 the US Centers for Disease Control and Prevention, the Emerging Pandemic Threat programme of the US Agency for International Development’s (USAID/EPT),11 the European Union,12 the Wellcome Trust,2 the UK-based Fleming Fund,13 and the international Global Health Security Agenda.14 It has been a focus of discussion at diverse international meetings, including the Davos, Switzerland Economic Summit15 and Thailand’s Prince Mahidol Award Conferences.16 The USAID/EPT programme has fostered the development of two One Health university networks—SEAOHUN in South-East Asia, and OHCEA in Eastern and Central Africa—that are engaged in One Health workforce development in those regions.17 Despite such widespread and growing acceptance, the One Health approach has been criticised for an excessive focus on emerging zoonotic diseases, inadequate incorporation of environmental concepts and expertise,18 and insufficient incorporation of social science and behavioural aspects of health and governance.19 20 Reviews of the burgeoning One Health literature have noted persistent scientific silos between human, animal and environmental sectors,21 the fact that many papers purporting to use a One Health approach actually consider only human and animal health (leaving out environmental health considerations),22 and that a need remains for additional proof-of-concept demonstrations on the added value of simultaneously considering human, animal and environmental health issues and outcomes in a One Health framework.23 24 To address such concerns, the recently published Checklist for One Health Epidemiological Reporting of Evidence,25 registered on the EQUATOR (Quality and Transparency in Health Research) network,26 encourages greater rigour and transparency in the reporting of One Health epidemiological research. How then does One Health relate to Planetary Health? In a recent review, Lerner and Berg27 define One Health as a concept that values interdisciplinarity, public health, animal health and ecosystem health. The related concept of EcoHealth is seen as focusing, primarily, on biodiversity as well as participatory knowledge-to-action approaches. Planetary Health, by contrast, in Lerner and Berg’s27 opinion, has a more ‘anthropocentric’ perspective, viewing ecosystems (including animals as part of the biotic environment) largely in terms of their contribution to human health, well-being and sustainability. One Health as a systems approach incorporating Planetary and EcoHealth concepts While the importance of emerging zoonotic diseases should be obvious to the readers of BMJ Global Health, we argue for further development of the One Health framework to better incorporate Planetary and EcoHealth concepts and the sense of urgency regarding environmental support systems. This expanded One Health framework builds on earlier systems approaches to human health, such as the biopsychosocial model of health proposed by Engel in the 1970s.28 In the biopsychosocial model (figure 1), human health is presented as a hierarchically organised system of increasing complexity, going from molecular interactions at the subcellular level, to tissues, organs and eventually individual humans. Many of these interactions on the lower end of the hierarchy, such as gene expression and medication effects, are the domain of systems biology and much of the practice of clinical medicine. The biopsychosocial model continues vertically towards levels of greater complexity, including interactions of humans in family groups, communities and larger societies. These more macroscopic interactions, and strategies to address population health at the community, national and global levels, relate more to the fields of public health, psychology and the social sciences, including economics and political science. Figure 1 Hierarchically organised system of human health, adapted from Engel.28 Our vision of One Health expands on this single hierarchical system of human health, to include simultaneously the three interconnected systems of humans, animals and the environment (figure 2). Like the biopsychosocial model, each system is organised vertically in levels of increasing complexity, from very simple molecular components up to complex systems of the global biosphere and the global populations of humans and animals. Figure 2 System levels for different types of One Health interactions. According to this framework, the One Health approach deals with the health-related interactions that occur between these systems at differing levels of complexity. Such interactions can take place at a molecular or cellular level: for example, the effect of environmental chemical exposures on cell receptors of humans or animals, or the exchange of antibiotic resistance genes between microbial communities of humans, animals or the environment. As with the biopsychosocial model for human health, many of these interactions can be described with systems biology or pathogen biology. Interactions can also occur at an individual level, such as the direct contact between a human and a companion animal in a household, and may require clinical interventions such as treatment of infection. At higher levels of interactions, such as community, national, regional and global population levels, other tools such as epidemiology, social and behavioural sciences, as well as atmospheric and geological sciences, and ‘big data’ expertise and approaches will be required. In this way, the One Health approach can ‘zoom out’ to address macrolevel or ‘planetary’-level interactions, such as the combined effect of growing human and animal populations on greenhouse gas emissions at the global/biospheric scale. Scaling from pathogens to populations One advantage of this expanded One Health framework is that it emphasises how interactions at clinical and local public health levels, such as emerging infectious diseases in individuals, households or communities, are connected to higher level, more complex threats to health and sustainability, including factors such as climate change, deforestation, and how they are impacted through land and water use, types of food production, human behaviours, poverty, equity and governance. As an example, characterisation of outbreaks of the zoonotic disease, Ebola, can be made at the individual level, where it is infecting humans, non-human primates and other animals. At this level, transmission events occur due to different types of contacts among and between humans and animals (eg, hunting, occupational, cultural practices, species-specific susceptibility and contaminated environmental sources). Addressing these problems involves knowledge of the viral transmission pathways and reducing contact between infected and susceptible individuals. At the more macroscopic level, however, the scope and severity of recent Ebola outbreaks may be related to deforestation, which is connected to local food insecurity and other uses of forests by expanding human and livestock populations, which are related in turn to cultural beliefs and practices, governance challenges and economic pressures. At a higher, national level, organisation of public health and economic systems affects education levels, access to healthcare and nutritious, affordable foods, and demographic trends including urbanisation and greater travel between villages and cities. These factors all have implications for agricultural systems and road building that affect the environment as well as both livestock and wildlife populations. Scaling up further involves consideration of regional changes in biodiversity and climate and the effect on bat reservoirs of the virus, and the effect of global travel patterns in moving the virus over large distances. Animals as sentinels In another scenario, a disease outbreak in an animal population, such as a sudden stranding of whales or other marine mammals, can capture the attention of the media and the public, raise questions on the causes of unexpected die-offs, and provide windows of opportunity for instituting needed, urgent solutions. While investigation of such events sometimes reveals a discrete proximate cause such as a viral infection or a toxic exposure, such a ‘sentinel event’ in animals may be an indicator of higher level environmental and human forces at play. Figure 3 shows how an animal sentinel event at an individual or group level can be mapped to larger, often planetary-level forces, resulting in improved articulation of research questions and more effective solutions. For example, accumulation of plastics found in the stomach of a stranded marine mammal may be a sign of wider contamination of marine environments by microplastics related to changes in the use of plastics in the textile industry.29 Widespread pollution by microplastics has considerable economic ramifications, including concerns about unsustainable manufacturing processes that could be affecting aquatic ecosystems, including fisheries important to the human food supply. Addressing this problem, therefore, may require major changes on the part of manufacturers and consumers, involving national and international policy initiatives. Figure 3 How sentinel events in animals and humans can provide warning of health threats at higher global and planetary levels. In another example, the outbreak of mercury poisoning among fish-eating residents of Minamata, Japan, due to contamination in local fish from the polluted bay30 was preceded by die-offs of fish and neurological disease events in cats and other animals. The event also showed the health danger of unregulated industrial manufacturing and widespread chemical pollution of the environment. Sustainable coexistence: humans and animals sharing environments The One Health framework can be used not just to identify and control health threats, but also to identify positive models for healthy coexistence, well-being and sustainability of these interconnected systems. For example, a farm with animals, if managed using One Health principles that optimise the health and well-being of the humans (farm workers, farm families, community members and consumers) as well as the animals and the local environment (protecting forests and water supplies, reducing energy consumption, using renewable energy, and eliminating air and chemical pollution) can provide a model that, if replicated on a wider scale, could help mitigate the environmental consequences of agricultural food production. Assessing the sustainability of different types of farming practices in a One Health way requires skills of modelling and integration of human, animal and environmental outcomes on a larger scale, considering aspects such as carbon footprint and life-cycle assessment. Why animal health matters A recent European consensus statement described the key aspects of the One Health concept as interspecies equity (valuing animal health and well-being simultaneously with humans), stewardship and resilience.31 Yet why should the global health community concern itself with animal health issues? It could be argued that, given the urgency of environmental degradation described in the Planetary Health report, higher priority should go to actions that focus on the survival of humans. In this worldview, animals are viewed as part of the life-supporting environment, contributing to the rich and complex biodiversity of ecosystems (necessary for the survival, well-being and health of humans and other species) and providing nutrition for human populations (at the pinnacle of the food chain). Yet there are important reasons to apply instead a One Health framework that places intrinsic value on considering the health and well-being of animals separate from environmental considerations. For one, the increasing number and rate of zoonotic disease events are directly related to the way that humans are managing land use, and wild and domestic animal populations, and therefore are likely to continue to occur. Simplistic solutions to zoonotic disease threats such as attempting to cull wildlife32 have proven futile in the past and are now understood to result in many negative unintended consequences for local people. Instead, we need to devise new and innovative methods of human coexistence with animals that will necessitate close cooperation between human, animal and environmental health professionals and other disciplines. Second, the relationship between animals and humans offers important economic and societal impacts, including many positive aspects in relation to non-communicable disease and health that are not adequately covered by a narrow focus on zoonotic disease.33 An example is our growing understanding that contact with animals may have effects on the human microbiome that could have a beneficial impact on the risk of allergies and asthma.34 Third, as discussed above, animals can be the canary in the coal mine warning us of new threats from environmental change. Ignoring such disease events risks or placing a low priority to investigating and understanding them risks delays in our understanding of the health implications of a changing environment. Fourth, there is a growing ethical discussion about the intrinsic value of animal life as well as animal welfare that seems likely to continue, making it important to consider issues such as animal well-being when designing policies related to environmental sustainability or control of specific disease threats.35 Lastly, the human affection and attachment to animals that has evolved over thousands of years is also likely to continue, and can be a critical leverage point in finding ways to promote policy, family and individual actions to protect the ecosystems we depend on for life. For example, the Planetary Health report mentions the paradox of certain global burden of disease indicators currently improving despite the many warning signs of environmental degradation. By contrast, the increase in animal disease outbreaks and species extinctions, clearly with important environmental change drivers, may be easier for the public to connect with. This could help drive support for policy change. Connecting global health to sustainability This ‘planetary’ vision for One Health, therefore, encompasses important aspects of both the One Health and Planetary Health frameworks that facilitate going from ‘local to global’, or more accurately ‘molecular to planetary’, to address the health, well-being and sustainability of humans, animals and the environment. This allows for consideration of a wide range of local solutions to complex health challenges rather than a ‘one size fits all’ prescription that could result from a top-down approach.33 Employing a comprehensive One Health framework encourages multidisciplinarity in global health research, education, programme and policy assessments, planning, and implementation. It also requires further development of useful metrics for tracking One Health outcomes,36 as well as better ways to assess impact.31 We encourage discussion and further development of this planetary One Health approach, and BMJ Global Health welcomes submissions based on the planetary One Health approach. Adopting the planetary vision for One Health will help to better connect ongoing global health efforts in disease control and preparedness to larger underlying and pressing issues of environmental change, equity and sustainability. Creating local models of healthy coexistence between humans and animal populations and the environments they share and depend on for life is critical for ensuring a sustainable future for our shared home of planet earth.

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          Antibiotic resistance is the quintessential One Health issue

          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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            Plastic microfibre ingestion by deep-sea organisms

            Plastic waste is a distinctive indicator of the world-wide impact of anthropogenic activities. Both macro- and micro-plastics are found in the ocean, but as yet little is known about their ultimate fate and their impact on marine ecosystems. In this study we present the first evidence that microplastics are already becoming integrated into deep-water organisms. By examining organisms that live on the deep-sea floor we show that plastic microfibres are ingested and internalised by members of at least three major phyla with different feeding mechanisms. These results demonstrate that, despite its remote location, the deep sea and its fragile habitats are already being exposed to human waste to the extent that diverse organisms are ingesting microplastics.
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              Exposure to household furry pets influences the gut microbiota of infant at 3–4 months following various birth scenarios

              Background Early-life exposure to household pets has the capacity to reduce risk for overweight and allergic disease, especially following caesarean delivery. Since there is some evidence that pets also alter the gut microbial composition of infants, changes to the gut microbiome are putative pathways by which pet exposure can reduce these risks to health. To investigate the impact of pre- and postnatal pet exposure on infant gut microbiota following various birth scenarios, this study employed a large subsample of 746 infants from the Canadian Healthy Infant Longitudinal Development Study (CHILD) cohort, whose mothers were enrolled during pregnancy between 2009 and 2012. Participating mothers were asked to report on household pet ownership at recruitment during the second or third trimester and 3 months postpartum. Infant gut microbiota were profiled with 16S rRNA sequencing from faecal samples collected at the mean age of 3.3 months. Two categories of pet exposure (i) only during pregnancy and (ii) pre- and postnatally were compared to no pet exposure under different birth scenarios. Results Over half of studied infants were exposed to at least one furry pet in the prenatal and/or postnatal periods, of which 8% were exposed in pregnancy alone and 46.8% had exposure during both time periods. As a common effect in all birth scenarios, pre- and postnatal pet exposure enriched the abundance of Oscillospira and/or Ruminococcus (P < 0.05) with more than a twofold greater likelihood of high abundance. Among vaginally born infants with maternal intrapartum antibiotic prophylaxis exposure, Streptococcaceae were substantially and significantly reduced by pet exposure (P < 0.001, FDRp = 0.03), reflecting an 80% decreased likelihood of high abundance (OR 0.20, 95%CI, 0.06–0.70) for pet exposure during pregnancy alone and a 69% reduced likelihood (OR 0.31, 95%CI, 0.16–0.58) for exposure in the pre- and postnatal time periods. All of these associations were independent of maternal asthma/allergy status, siblingship, breastfeeding exclusivity and other home characteristics. Conclusions The impact of pet ownership varies under different birth scenarios; however, in common, exposure to pets increased the abundance of two bacteria, Ruminococcus and Oscillospira, which have been negatively associated with childhood atopy and obesity. Electronic supplementary material The online version of this article (doi:10.1186/s40168-017-0254-x) contains supplementary material, which is available to authorized users.
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                Author and article information

                Journal
                BMJ Glob Health
                BMJ Glob Health
                bmjgh
                bmjgh
                BMJ Global Health
                BMJ Publishing Group (BMA House, Tavistock Square, London, WC1H 9JR )
                2059-7908
                2018
                2 October 2018
                : 3
                : 5
                : e001137
                Affiliations
                [1 ] departmentDepartment of Environmental and Occupational Health Science, Department of Global Health, Department of Family Medicine, Department of Medicine, Division of Allergy and Infectious Disease , Center for One Health Research, University of Washington , Seattle, Washington, USA
                [2 ] departmentDepartment of Environmental and Occupational Health Sciences , Center for One Health Research, University of Washington , Seattle, Washington, United States
                [3 ] departmentDepartment of Anthropology, Department of Environmental and Global Health , Emerging Pathogens Institute, University of Florida , Gainesville, FL, United States
                [4 ] Florida Department of Agriculture and Consumer Services , Tallahassee, Florida, USA
                Author notes
                [Correspondence to ] Professor Peter MacGarr Rabinowitz; peterr7@ 123456uw.edu
                Article
                bmjgh-2018-001137
                10.1136/bmjgh-2018-001137
                6169660
                30294465
                51504b5b-cf48-4605-a2ad-4acb82d4b57a
                © Author(s) (or their employer(s)) 2018. Re-use permitted under CC BY-NC. No commercial re-use. See rights and permissions. Published by BMJ.

                This is an open access article distributed in accordance with the Creative Commons Attribution Non Commercial (CC BY-NC 4.0) license, which permits others to distribute, remix, adapt, build upon this work non-commercially, and license their derivative works on different terms, provided the original work is properly cited, appropriate credit is given, any changes made indicated, and the use is non-commercial. See: http://creativecommons.org/licenses/by-nc/4.0/

                History
                : 24 August 2018
                : 24 August 2018
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                environmental health,one health,planetary health,zoonoses,animal sentinels,ecohealth

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