Science Selection August 2013 | Volume 121 | Issue 8
Germ Warfare? Strategies for Reducing the Spread of Antibiotic Resistance
Carol Potera, based in Montana, has written for EHP since 1996. She also writes for Microbe, Genetic Engineering News, and the American Journal of Nursing.
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A growing body of literature describes how human pathogens in the environment acquire antibiotic resistance genes (ARGs), a process potentially boosted by selection pressure from antibiotics. Contaminated water and soil may then maintain and spread these antibiotic-resistant bacteria (ARB) and ARGs. A review in this issue of EHP examines strategies for reducing environmental pollution with antibiotics, ARBs, and ARGs from various sources, including traditional agriculture, aquaculture, wastewater treatment plants (WWTPs), pharmaceutical manufacturers, and hospitals.1
“This information needs to reach a wider audience, especially in the medical and public health fields,” says coauthor Amy Pruden, a professor of civil and environmental engineering at Virginia Tech in Blacksburg.
Limiting antibiotics in animal production is the most direct way to control environmental ARB and ARGs, according to the authors.1 After Denmark banned antibiotics as animal growth promoters in 1998, investigators found marked reductions of antibiotic resistance. During the period 1997–2000, erythromycin resistance in Enterococcus faecium fell from 76% to 13% in Danish broiler chickens and from 90% to 47% in pigs, suggesting that regulations can be useful in reversing antibiotic resistance in food animals.2 In the United States, 70% of antibiotics are given to farm animals, largely to promote growth, not treat disease.
Good animal husbandry practices, such as low animal density and good nutrition, keep animals healthy and reduce the need for antibiotics.3 Immunizing farm animals and fish with inexpensive vaccines aimed at major animal pathogens would further limit the need for antibiotics.1 Adoption of salmon vaccines in Norway facilitated a 99% reduction in antimicrobial use between 1987 and 2007, and fish production soared from 350,000 to 850,000 metric tons during the same time.4 Overall, “there is a need for cheap and effective animal vaccines,” says coauthor Joakim Larsson, a professor of environmental pharmacology at the University of Gothenburg, Sweden.
Antibiotics, ARB, and ARGs from farm animals, households, hospitals, and drug manufacturers often end up at WWTPs. These facilities are designed primarily to remove solid organic matter, nitrogen, and phosphorus, although some also apply disinfectants to kill bacteria.1,5 WWTP processes secondarily remove some ARB and ARGs, although with some treatment methods ARGs have been shown to rebound during subsequent treatment.6 At least 56 antibiotics from 6 drug classes have been detected in treated sewage.7
WWTPs hold promise as a critical point for removing ARB and ARGs by biodegradation, adsorption, chemicals, and other effective and economical modifications. “More research is needed to identify which treatments are most effective to better design WWTP operations,” says Pruden.
Certain drug manufacturing hubs have been identified as “hot spots” that release high levels of antibiotics, ARB, and ARGs into surface, ground, and drinking water.8 The authors write that “a range of treatment technologies” will be necessary to address industrial production. However, they add, it’s not all about identifying or developing technical solutions—it also is important to create incentives to apply these technical solutions. As an example, they cite Sweden’s implementation of new environmental criteria in the procurement and reimbursement systems hospitals use to purchase medicines.1
“All solutions must start with changes in local practices and then be implemented at a global scale, or we will get nowhere,” says coauthor David Graham, a professor of ecosystems engineering at Newcastle University, United Kingdom. The problem of antibiotic resistance “will only be reduced if we change our behavior at all fronts,” Graham says. “Greater control of the medical and agricultural uses of antibiotics must be coupled with greater control of our wastes.”
Marilyn C. Roberts, a professor of environmental and occupational health sciences at the University of Washington in Seattle, commends the review authors for presenting “the big picture,” but she says providing specific details about what individuals can do would have been a valuable addition. For example, people could demand that food labels state whether food was grown with antibiotics and list the levels of antibiotic residues in a food. “This information would allow consumers to choose not to select products that use antibiotics and/or have measurable amounts of antibiotic residues,” Roberts says.
Antibiotic resistance is now making an appearance on Capitol Hill. A bill titled Strategies to Address Antimicrobial Resistance (STAAR) was reintroduced to the U.S. House of Representatives in June 2013.9 STAAR was originally introduced in both chambers in 2007 but died in committee.10,11 The House bill was reintroduced in 2009 but once again failed. The legislation would establish an Office of Antimicrobial Resistance and strengthen funding for related research.
1. Pruden A, et al. Management options for reducing the release of antibiotics and antibiotic resistance genes to the environment. Environ Health Perspect 121(8):878–885 (2013); http://dx.doi.org/10.1289/ehp.1206446.
2. Aarestrup FM, et al. Effect of abolishment of the use of antimicrobial agents for growth promotion on occurrence of antimicrobial resistance in fecal enterococci from food animals in Denmark. Antimicrob Agents Chemother 45(7):2054–2059 (2001); http://dx.doi.org/10.1128/AAC.45.7.2054-2059.2001.
3. van de Weerd HA, et al. A review of key health-related welfare issues in organic poultry production. World Poult Sci J 65(4):649–684 (2009); http://dx.doi.org/10.1017/S0043933909000464.
4. Heuer OE, et al. Human health consequences of use of antimicrobial agents in aquaculture. Clin Infect Dis 49(8):1248–1253 (2009); http://dx.doi.org/10.1086/605667.
5. Leong LYC, et al. Wastewater Treatment and Reuse: Final Report. Disinfection of Wastewater Effluent—Comparison of Alternative Technologies. Alexandria, VA:Water Environment Research Foundation (2008). Available: http://goo.gl/bJg6E [accessed 16 July 2013].
6. Ma Y, et al. Effect of various sludge digestion conditions on sulfonamide, macrolide, and tetracycline resistance genes and class I integrons. Environ Sci Technol 45(18):7855–7861 (2011); http://dx.doi.org/10.1021/es200827t.
7. Zhang T, Li B. Occurrence, transformation, and fate of antibiotics in municipal wastewater treatment plants. Crit Rev Environ Sci Technol 41(11):951–998 (2011); http://dx.doi.org/10.1080/10643380903392692.
8. Fick J, et al. Contamination of surface, ground, and drinking water from pharmaceutical production. Environ Toxicol Chem 28(12):2522–2527 (2009); http://dx.doi.org/10.1897/09-073.1.
9. H.R. 2285 (113th Congress): Strategies to Address Antimicrobial Resistance Act. Available: http://www.govtrack.us/congress/bills/113/hr2285 [accessed 16 July 2013].
10. H.R. 3697 (110th Congress): Strategies to Address Antimicrobial Resistance Act. Available: http://www.govtrack.us/congress/bills/110/hr3697 [accessed 16 July 2013].
11. S. 2313 (110th Congress): Strategies to Address Antimicrobial Resistance Act. Available: http://www.govtrack.us/congress/bills/110/s2313 [accessed 16 July 2013].
EHP is pleased to present the abstracts from the 29th Annual Scientific Conference of the International Society for Environmental Epidemiology (ISEE), held in Sydney, Australia, 24–28 September 2017. The conference was hosted by The University of Sydney and cosponsored by the Woolcock Institute of Medical Research, with the theme “Healthy Places, Healthy People—Where Are the Connections?”
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