Proteus mirabilis PM13 is a well characterized chloramphenicol-sensitive isolate which spontaneously gives rise to resistant colonies on solid media containing chloramphenicol (50ug/ml) at a plating efficiency of between 10-4 and 10-5 per cell per generation. When a chloramphenicol resistant colony is grown in liquid medium in the absence of the antibiotic for I50 generations a population of predominantly sensitive cells arises. The cat gene responsible for the phenomenon is chromosomal, and has been cloned from P.mirabilis PMI3 with DNA prepared from cells grown in the absence or the presence of chloramphenicol. Recombinant plasmids which confer resistance to chloramphenicol carry an 8.5-kb PstI fragment irrespective of the source of host DNA. The location of The cat gene within the PstI fragment was determined by Southern blotting with a cat consensus 'active - site' oligonucleotide (5'-CCATCACAGACGGCATGATG-3') corresponding to the expected amino acid sequence of the active site region of chloramphenicol acetyltransferase. DNA sequence analysis has revealed a high degree of homology between the P. mirabllls cat -gene and the type I ca-t variant (Tn9), 76% at the amino acid level and 73% when nucleotides in the coding sequence are compared. The mechanism for the appearance and disappearance of chloramphenicol resistance in P. mirabilis appears to be associated with a host-specific trans-acting element which controls cat gene expression. A precedent for such a control network is given by phase variation in Salmonella typhimurium, where an invertible DNA segment controls the transcription of a trans-acting regulatory element. A comparison of the 5' regions of the S.typhimurium flagellin genes in and H2, which are alternately expressed by a flip-flop control mechanism with the 5' region of P.mirabilis cat show blocks of homology. Whether or not this homology is significant in the regulation of cat gene expression has not been determined.

Les bactéries de l'environnement et du sol en particulier sont des producteurs actifs de molécules antibiotiques et les composés antibiotiques utilisés en médecine ont pour la plupart été isolés de bactéries saprophytes du sol qui ont elle mêmes développé une variété de mécanismes pour contrer les effets des antibiotiques conduisant à un arsenal de gènes de résistance à des antibiotiques dans l'environnement (ARGD). Une évaluation de l'abondance et de la diversité en terme de gènes de résistance à des antibiotiques a donc été conduite. Pour cette analyse, nous avons compilé 71 jeux de données de séquences d'ADN métagénomique environnementale variées: océans, et identifié des gènes de résistance pour chacun d'eux. Le sol est confirmé par cette étude comme un environnement extrêmement divers en terme de résistance à des antibiotiques. Cet étude in silico a été complété d'abord par une approche en microcosmes visant à étudier les effets soit de pollution soit par des molécules antibiotiques pures, soit par des effluents de ferme utilisés pour la fertilisation des sols. Les microcosmes de sols ont été incubés pendant 6 mois au laboratoire en conditions contrôlées. L'abondance de gènes de résistance à des antibiotiques a été évaluée au cours du temps par PCR quantitative. Une seconde étude visant à évaluer l'impact de la consommation de molécules antibiotiques par une population humaine sur son environnement immédiat, dont le sol, a été entreprise. Le village de Trois-Sauts est situé sur les berges du haut-Oyapock en Guyane Française. Les prescriptions antibiotiques sont très récentes dans cette région et les molécules distribuées ont été précisément répertoriées. Un transect de sol de 3km a été échantillonné chaque 600m afin de vérifier l'existence d'un gradient d'anthropisation entre le village (0m) et les échantillons de forêt les plus distants (3000m). Tous nos résultats confirment la présence à une forte abondance de gènes de résistance à des antibiotiques dans l'environnement, et en particulier dans le sol. Les facteurs à l'origine de la sélection et de la dissémination des gènes de résistance restent cependant difficiles à appréhender dans des environnements aussi complexes. C'est cependant avec une meilleure compréhension des phénomènes conduisant à l'émergence et à la dissémination des gènes de résistance à des antibiotiques au sein des flores pathogènes, depuis leur réservoir environnemental, que nous pourrons agir en vue de préserver les antibiotiques encore actifs aujourd'hui et ceux encore à développer. / Environmental bacteria and especially soil bacteria are active producers of antibiotic molecules and most drugs used nowadays are isolated from saprophytic soil bacteria and these microorganisms have also evolved numerous resistance pathways leading to an arsenal of Antibiotic Resistance Genes Determinants (ARGD) known as the environmental resistome. A survey of ARGD prevalence is required in order to characterize this natural phenomenon with critical implications in our current infectious diseases management. In order to perform such analysis we compiled a set of 71 metagenomic datasets from various environmental origins: soils, oceans, lakes, human feces, indoor air, etc., and compared their sequences with a database of known antibiotic resistance gene determinants (ARGD). ARGD-annotated reads are found in every environment analyzed confirming their ubiquity. Soil is found to be the richest and shares a large part of ARGD with the human gut microbiome, indicating ARGD transfers between these environments. Experiments using qPCR and metagenomic DNA sequencing on soil samples from two sites with known and distinct antibiotic pollution history were conducted to understand how ARGD abundance and diversity in soil are affected when impacted by antibiotic molecules. The first site is a reference soil from a long-term experiment without history of antibiotic pollution (Rothamsted Park Grass, UK). Soil microcosms are setup with addition of either antibiotic-containg animal manure or pure molecules and incubated for 6 months to monitor changes in ARGD concentration following these perturbations. Our second study-site is a very remote settlement in French Guiana where antibiotics are available since recently and may have impacted the local soil microbial community. Soil samples are taken following a line-transect going from the village (antibiotic source) to 3km deep in the forest in a gradient of human-impact. Our results all confirm prevalence of ARGD in soil at significant abundance but also that ARGD distribution is more correlated to environmental factors such as soil type, microbial taxonomy composition or microcosms incubation conditions than antibiotic molecules exposure in both sites. Pathogens ARGD diversity is far lower than ARGD diversity found in the environment and not all the soil resistome is readily accessible for transfer. In order to characterize the soil mobile gene pool, a strategy is proposed to isolate specifically mobile DNA directly from the environment for sequencing purposes. Better knowledge on the microbial ecology factors limiting ARGD transfers to pathogens may greatly help us reduce the current threat on our limited medical antibiotic molecules resource.

Antibiotic resistance is currently a global threat spanning clinical, environmental, and geopolitical research domains. The environment is increasingly recognized as a key node in the spread of antibiotic resistance genes (ARGs), which confer antibiotic resistance to bacteria. Detecting ARGs in the environment is the first step in monitoring and controlling antibiotic resistance. In recent years, next-generation sequencing of environmental samples (metagenomic sequencing data) has become a prolific tool for the field of surveillance. Metagenomic data are nucleic acid sequences, or nucleotides, of environmental samples. Metagenomic sequencing data has been used over the years to detect and analyze ARGs. An intriguing instance of ARGs is the multi-functional ARG, where one ARG encodes two or more different antibiotic resistance functions. Multi-functional ARGs provide resistance to two or more antibiotics, thus should have evolutionary advantage over ARGs with resistance to single antibiotic. However, there is no tool readily available to detect these multi-functional ARGs in metagenomic data. In this study, we develop a computational pipeline to detect multi-functional ARGs in metagenomic data. The pipeline takes raw metagenomic data as the input and generates a list of potential multi-functional ARGs. A plot for each potential multi-functional ARG is also created, showing the location of the multi-functionalities in the sequence and the sequencing coverage level. We collected samples from three different sources: influent samples of a wastewater treatment plant, hospital wastewater samples, and reclaimed water samples, ran the pipeline, and identified 19, 57, and 8 potentially bi-functional ARGs in each source, respectively. Manual inspection of the results identified three most likely bi-functional ARGs. Interestingly, one bi-functional ARG, encoding both aminoglycoside and tetracycline resistance, appeared in all three data sets, indicating its prevalence in different environments. As the amount of antibiotics keeps increasing in the environment, multi-functional ARGs might become more and more common. The pipeline will be a useful computational tool for initial screening and identification of multi-functional ARGs in metagenomic data. / Master of Science / Antibiotics are the drug to fight against the infection of bacteria. Since the first antibiotic was discovered in 1928, many antibiotic drugs have been developed. At the same time, scientists discovered many genes responsible for the resistance of antibiotic drugs. Nowadays, antibiotic resistance is a global threat. Detecting antibiotic resistance genes in the environment is the first step toward monitoring and controlling antibiotic resistance. In recent years, next-generation sequencing has been widely used to get the DNA sequence from the environment. Metagenomics analysis has been used over the years to detect and analyze ARGs. In the literature, it has been reported that a single gene could carry two parts of sequences corresponding to two different ARGs, thus conferring resistance to two different antibiotics. This fusion might have some evolutionary advantages. In this study, we developed a novel computational tool to detect multi-functional ARGs. We collected data from three sources: the treatment plant water, the hospital wastewater, and the reclaimed water, and identified 19, 57, and 8 potential bi-functional ARGs in each source, respectively. After we manually inspected the result, we found three most likely bi-functional ARGs. We also found one bi-functional ARG that appears in all three datasets. The gene is responsible for aminoglycoside and tetracycline resistance. The tool will serve as the initial screening step to detect multi-functional ARGs.

The ubiquitous nature of antibiotic resistance and antibiotic resistance genes (ARGs) among environmental pathogens from a variety of wastewater effluents, suggests that the aquatic environment, and specifically alternative wastewater treatment systems, may act as reservoirs for drug resistant bacteria and ARGs, thereby contributing to the widespread dissemination of antibiotic resistance. More research is necessary to contribute to our understanding of the occurrence, fate, and mobility of antibiotic resistance and ARGs among bacterial indicators of faecal contamination as well as pathogenic bacteria within Canadian wastewater treatment systems. The primary objective of this research was to determine the prevalence, fate, and potential transfer of bacterial resistance and ARGs among selected environmental pathogens exposed to alternative wastewater treatment systems, while considering the impact of treatment strategies on the expression of antibiotic resistance. A detailed analysis was initially conducted with respect to the characterization and quantification of microbial populations (including antibiotic resistant bacteria) in a variety of treatment systems and waste effluent sources. Traditional culture-based screening techniques in combination with molecular characterization (through colony or multiplex PCR), and molecular quantification using real-time quantitative PCR were utilized in order to help establish a preliminary environmental assessment of selected pathogens (Escherichia coli, Enterococcus spp., Salmonella spp.) and ARGs (tetA, blaSHV, & ampC) within a variety of wastewater treatment systems (lab-scale mesocosms, constructed wetland, constructed lagoon system, and pilot-scale biological nutrient removal (BNR) system). Overall, the level of multiple antibiotic resistance (MAR) among culturable indicator (E. coli & Enterococcus spp.) and environmental bacteria was high (reaching 100% in several instances) within different types of wastewater treatment systems and effluent sources (poultry waste effluent, municipal wastewater, aquaculture wastewater). Common antibiotic resistance profiles among E. coli isolates included simultaneous resistance to between three and five antimicrobials, whereas common MAR profiles among Enterococcus spp. isolates showed resistance to ten or more antibiotics. Real time quantitative PCR was used to determine the concentration of three bacterial pathogens; E. coli, Enterococcus faecalis, and Salmonella spp., and three ARGs; tetA, ampC, and blaSHV, within a variety of wastewater samples. Based on the results, it was concluded that high concentrations of ARGs were present in the treated effluent (10⁴- 10⁶ target gene copies/100 mL), regardless of system type (i.e. constructed lagoon, pilot-scale BNR, or constructed wetland), which may ultimately serve as a potential route for entry of ARGs and antibiotic resistant bacteria into the natural environment. Water is considered an important medium for transfer of resistance genes and resistant bacteria to the broader environment. Few studies have examined the transferability via conjugation of ARGs in E. coli and Salmonella spp. isolated from wastewater. Identification of three resistance determinants (tetA, strA, strB) conferring resistance to tetracycline and streptomycin was performed on selected multi-drug resistant Salmonella spp. and E. coli isolates. The potential for transfer of tetracycline and streptomycin resistance genes was demonstrated through broth conjugation experiments using multi-drug resistant Salmonella spp. and E. coli isolates as donors, and E. coli K12 as the recipient. Conjugation was successfully observed in 75% (9/12) of donor isolates, occurring in both Salmonella spp. and E. coli isolates. Six strains (50%) were capable of transferring their tetA, strA, and strB genes to the recipient strain, resulting in 58.5% (38/65) of total transconjugant strains acquiring all three resistance determinants. The results confirm the role of environmental bacteria (isolated from wastewater treatment utilities) as a reservoir of antibiotic resistance and ARGs, containing mobile genetic elements, which are capable of disseminating and transferring ARGs. As concerns about water quality and environmental contamination by human and agricultural effluents have increased, it has become increasingly more important to consider the prevalence and transferability of ARGs to opportunistic and human pathogens. As observed in this research, the ubiquitous nature of multi-drug resistant bacteria in water and wastewater effluents, the presence of diverse ARGs of human and veterinary health significance, as well as the transfer of resistance determinants through conjugative plasmids to recipient bacteria, suggests that environmental exposure through contact or consumption with contaminated water is probable. However, a lack of critical information still exists regarding the movement of resistance genes within and between microbial populations in the environment. In addition, the extent of human exposure to ARGs and antibiotic resistant bacteria is still not well understood, and future studies on human exposure to these resistant contaminants are necessary.

The ubiquitous nature of antibiotic resistance and antibiotic resistance genes (ARGs) among environmental pathogens from a variety of wastewater effluents, suggests that the aquatic environment, and specifically alternative wastewater treatment systems, may act as reservoirs for drug resistant bacteria and ARGs, thereby contributing to the widespread dissemination of antibiotic resistance. More research is necessary to contribute to our understanding of the occurrence, fate, and mobility of antibiotic resistance and ARGs among bacterial indicators of faecal contamination as well as pathogenic bacteria within Canadian wastewater treatment systems. The primary objective of this research was to determine the prevalence, fate, and potential transfer of bacterial resistance and ARGs among selected environmental pathogens exposed to alternative wastewater treatment systems, while considering the impact of treatment strategies on the expression of antibiotic resistance. A detailed analysis was initially conducted with respect to the characterization and quantification of microbial populations (including antibiotic resistant bacteria) in a variety of treatment systems and waste effluent sources. Traditional culture-based screening techniques in combination with molecular characterization (through colony or multiplex PCR), and molecular quantification using real-time quantitative PCR were utilized in order to help establish a preliminary environmental assessment of selected pathogens (Escherichia coli, Enterococcus spp., Salmonella spp.) and ARGs (tetA, blaSHV, & ampC) within a variety of wastewater treatment systems (lab-scale mesocosms, constructed wetland, constructed lagoon system, and pilot-scale biological nutrient removal (BNR) system). Overall, the level of multiple antibiotic resistance (MAR) among culturable indicator (E. coli & Enterococcus spp.) and environmental bacteria was high (reaching 100% in several instances) within different types of wastewater treatment systems and effluent sources (poultry waste effluent, municipal wastewater, aquaculture wastewater). Common antibiotic resistance profiles among E. coli isolates included simultaneous resistance to between three and five antimicrobials, whereas common MAR profiles among Enterococcus spp. isolates showed resistance to ten or more antibiotics. Real time quantitative PCR was used to determine the concentration of three bacterial pathogens; E. coli, Enterococcus faecalis, and Salmonella spp., and three ARGs; tetA, ampC, and blaSHV, within a variety of wastewater samples. Based on the results, it was concluded that high concentrations of ARGs were present in the treated effluent (10⁴- 10⁶ target gene copies/100 mL), regardless of system type (i.e. constructed lagoon, pilot-scale BNR, or constructed wetland), which may ultimately serve as a potential route for entry of ARGs and antibiotic resistant bacteria into the natural environment. Water is considered an important medium for transfer of resistance genes and resistant bacteria to the broader environment. Few studies have examined the transferability via conjugation of ARGs in E. coli and Salmonella spp. isolated from wastewater. Identification of three resistance determinants (tetA, strA, strB) conferring resistance to tetracycline and streptomycin was performed on selected multi-drug resistant Salmonella spp. and E. coli isolates. The potential for transfer of tetracycline and streptomycin resistance genes was demonstrated through broth conjugation experiments using multi-drug resistant Salmonella spp. and E. coli isolates as donors, and E. coli K12 as the recipient. Conjugation was successfully observed in 75% (9/12) of donor isolates, occurring in both Salmonella spp. and E. coli isolates. Six strains (50%) were capable of transferring their tetA, strA, and strB genes to the recipient strain, resulting in 58.5% (38/65) of total transconjugant strains acquiring all three resistance determinants. The results confirm the role of environmental bacteria (isolated from wastewater treatment utilities) as a reservoir of antibiotic resistance and ARGs, containing mobile genetic elements, which are capable of disseminating and transferring ARGs. As concerns about water quality and environmental contamination by human and agricultural effluents have increased, it has become increasingly more important to consider the prevalence and transferability of ARGs to opportunistic and human pathogens. As observed in this research, the ubiquitous nature of multi-drug resistant bacteria in water and wastewater effluents, the presence of diverse ARGs of human and veterinary health significance, as well as the transfer of resistance determinants through conjugative plasmids to recipient bacteria, suggests that environmental exposure through contact or consumption with contaminated water is probable. However, a lack of critical information still exists regarding the movement of resistance genes within and between microbial populations in the environment. In addition, the extent of human exposure to ARGs and antibiotic resistant bacteria is still not well understood, and future studies on human exposure to these resistant contaminants are necessary.

Antimicrobial resistance (AMR) is a One-Health (human, animal, environment) challenge that requires collaborative, interdisciplinary action. Comparable surveillance data are needed to effectively inform policy interventions aimed at preventing the spread of AMR. Environmental monitoring lags behind that of other One Health sectors and is in need of agreed upon targets and standardized methods. A challenge is that there are numerous microorganisms, antibiotic resistance genes (ARGs), and mobile genetic elements and corresponding methods that have been proposed. In this dissertation, a framework for AMR monitoring of aquatic environments was developed through a combination of literature review and stakeholder input, via surveys and a workshop. Through this process, three targets were selected for standardization: the sulfonamide resistance gene (sul1), the class 1 integron integrase gene (intI1), and cefotaxime-resistant Escherichia coli. Quantitative polymerase chain reaction (qPCR)- and culture-based protocols were developed and pilot tested in two independent laboratories on a set of six water matrices: wastewater, recycled water, and surface water from six different wastewater utilities engaging in water reuse located in five states across the USA. The impact of wastewater treatment and advanced water treatment processes was examined in terms of removal of these targets. Finally, qPCR and culture methods were used to examine the relationship between sul1, intI1, E. coli, and fecal indicators in private household wells across four states in the Southern USA that were identified as susceptible to storm events. The overall findings provide a useful baseline occurrence of the proposed AMR monitoring indicators across a range of water types and protocols that are accessible to water utilities. / Doctor of Philosophy / Life-saving drugs and treatments are failing at an increasing rate because of antimicrobial resistance (AMR). Antimicrobials, such as antibiotics, are a double-edged sword, because they are an effective weapon for killing disease-causing pathogens, but the more they are used the greater the likelihood that microbes that are resistant to them will survive, reproduce, and spread. National action plans for AMR have been created by a majority of countries, emphasizing the importance of antibiotic stewardship and other mitigation strategies. However, numerous data gaps need to be addressed in order to identify strategies that are most likely to be effective and to implement them. Environmental surveillance, including wastewater influent, wastewater effluent, and surface water, could prove an informative means to track AMR trends with time and relate them to human activities and corresponding mitigation efforts. The purpose of this dissertation was to develop a framework for AMR surveillance of aquatic environments and to test it across an array of sample types. We considered an array of possible culture- and DNA-based targets from available scientific literature and engaged experts and stakeholders in narrowing down the list to options that were both informative and feasible. We developed protocols for quantifying an antibiotic resistance gene (sul1), a mobile genetic element that has been implicated in the spread of multi-antibiotic resistance (intI1), and an extended spectrum beta-lactamase (ESBL) producing form of Escherichia coli. We compared the methods between two independent laboratories on untreated wastewater, treated wastewater, recycled water, and surface water collected from six locations across five states. We additionally did a survey of private household well water that was hypothesized to be vulnerable to contamination due to storms and lack of resources for maintenance. The results of this research can help to support environmental monitoring of AMR across the US and globally.

Antibiotic resistance is a growing human health threat, making infections more difficult to treat and increasing fatalities from and cost of treatment of associated diseases. The rise of multidrug resistant pathogens threatens a return to the pre-antibiotic era where even the most common infections may be impossible to treat. It is estimated that the majority of global antibiotic use, and use in the U.S., is dedicated towards livestock, where they are used to promote growth, treat, or prevent disease. Given that exposure to antibiotics selects for antibiotic resistant bacteria (ARBs) and can stimulate the horizontal transfer of their associated antibiotic resistance genes (ARGs), it is important to examine livestock operations as a reservoir of resistance. Correspondingly, there is growing interest in identifying how agricultural practices can limit the potential for spread of antibiotic resistance through the "farm to fork continuum," starting with antibiotic use practices, manure management and land application and ending with the spread of ARBs and ARGs present onto edible crops and serving as a route of exposure to consumers. This study focused specifically on the effect of composting on the prevalence of ARBs and ARGs in cattle manure. Three composting trials were performed: small-scale, heat-controlled, and large-scale. The small-scale composting trial compared dairy and beef manures, with or without antibiotic treatment (treated beef cattle received chlortetracycline, sulfamethazine, and tylosin while treated dairy cattle received cephapirin and pirlimycin), subject to either static or turned composting. The heat-controlled composting trial examined only dairy manure, with or without antibiotic treatment, subject to static composting, but using external heat tape applied to the composting tumblers to extend the duration of the thermophilic (>55°C) temperature range. The large-scale composting trial examined dairy manure, with or without antibiotic treatment, subject to static composting at a much larger scale that is more realistic to typical farm practices. Samples were analyzed to assess phenotypic resistance using the Kirby Bauer disk diffusion method and by diluting and plating onto antibiotic-supplemented agar. Genetic markers of resistance were also assessed using quantitative polymerase chain reaction (qPCR) to quantify sul1 and tet(W) ARGs; metagenomic DNA sequencing and analysis were also performed to assess and compare total ARG abundance and types across all samples. Results indicate that composting can enrich indicators of phenotypic and genetic resistance traits to certain antibiotics, but that most ARGs are successfully attenuated during composting, as evidenced by the metagenomic sequencing. Maintaining thermophilic composting temperatures for adequate time is necessary for the effective elimination of enteric bacteria. This study suggests that indicator bacteria that survive composting tend to be more resistant than those in the original raw manure; however, extending the thermophilic stage of composting, as was done in the heat-controlled trial, can reduce target indicator bacteria below detection limits. Of the two ARGs specifically quantified via qPCR, prior administration of antibiotics to cattle only had a significant impact on tet(W). There was not an obvious difference in the final antibiotic resistance profiles in the finished beef versus dairy manure composts according to metagenomics analysis. Based on these results, composting is promising as a method of attenuating ARGs, but further research is necessary to examine in depth all of the complex interactions that occur during the composting process to maximize performance. If not applied appropriately, e.g., if time and temperature guidelines are not enforced, then there is potential that composting could exacerbate the spread of certain types of antibiotic resistance. / Master of Science

Since penicillin was discovered in 1928, antibiotic usage in human and veterinary medicine and prevalence of antibiotic resistant bacteria (ARB), has been increasing. While antibiotics and antibiotic resistance genes (ARGs) naturally occur in soils, increasing abundances of ARGs correlate with increased antibiotic usage in agricultural settings. When livestock are treated with antibiotics, the antibiotic compounds, ARB, and ARGs can enter soil via manure excreted onto pastures or applied to other fields as fertilizer, thereby spreading antimicrobial resistance (AMR) in the environment. In addition to human health implications, increased AMR has negative impacts on ecosystem services such as carbon and nitrogen cycling. While many studies have researched antibiotic persistence in agricultural systems and their impacts on soil microbial communities, there are still significant knowledge gaps around the long-term effects of antibiotic exposure in soils, how those impacts differ among soils, and how elements of AMR may differentially transport through soil. To address these knowledge gaps, our objectives were to 1) examine the impact of multi-year repeated additions of manure from cattle administered antibiotics on soil microbial communities, 2) determine the interactive effects of soil moisture and type on soil microbial communities exposed to antibiotics and manure, and 3) differentiate between vertical transport of AMR in the form of viable ARB or ARGs in extracellular plasmids. Our results demonstrate that soil bacterial community structures were consistently altered by 3-year additions of manure from cattle administered antibiotics compared to soil amended with antibiotic-free manure. Furthermore, ARG abundances were higher in soils with manure additions compared to soil without manure, although this was true regardless of whether the cattle were administered antibiotics, suggesting that manure and antibiotic impacts on soil microbial communities can persist over multi-year of repeated manure applications. Additionally, in microcosms, effects of manure from cattle administered antibiotics on ARG abundances, microbial community structures, respiration, and nitrogen pools in soil were seen across multiple soil types and moisture contents, suggesting environmental conditions can alter how manure and antibiotics impact microbial community structure and nutrient cycling. Finally, ARB flowed readily through saturated soil, but were also detectable in the top 5 cm of soil columns. However, ARGs on extracellular plasmids did not flow through soil columns and were not detected in soil, indicating that extracellular DNA does not persist or transport through the soil to any meaningful degree. Overall, these results indicate a nuanced approach is required to mitigate the environmental spread of AMR. Soil management strategies for addressing the AMR crisis should consider the broader context of manure management, as high ARG abundances can come from application of manure from antibiotic-free cattle, and soil microbial communities in individual environments may have varied responses to manure antibiotic exposure. Furthermore, the transport of AMR through soil is complex and dynamic, as elements of AMR may transport differently through soil and require separate consideration in modeling and management. Future AMR management practices that consider diverse factors that affect persistence and spread of AMR in the environment can help protect livestock productivity and maintain the efficacy of antibiotics to protect human and animal health. / Doctor of Philosophy / Antibiotics are an important tool used to fight infections in humans, pets, and livestock. As antibiotics are used more frequently, the bacteria they target are more likely to develop resistance to the antibiotics, leading to increasing cases of infections that are harder to treat and higher risk. Antibiotic resistance can persist and spread in multiple forms, including the antibiotic compounds themselves, as antibiotic resistant bacteria (ARB), or as the genetic material that encodes for antibiotic resistance genes (ARGs). In agricultural systems, when livestock are treated with antibiotics they can excrete the antibiotics, along with ARB and ARGs, in the manure, which is then applied to land as fertilizer. In addition to the associated health risks, the spread of antibiotic resistance impacts microscopic bacteria and fungi in the soil, which are important for recycling nutrients for plants and maintaining ecosystem health. The overall goal of this dissertation was to gain a better understanding of how manure from cattle given antibiotics impacts these bacteria and fungi when manure is applied to the soil. The specific objectives were to 1) look impacts after long-term (multiple years) of manure addition, 2) examine how bacteria and fungi might respond differently to antibiotics in soils of different type or with different amounts of water, and 3) determine if ARGs that exist as free genetic material outside of living bacteria can be moved through the soil with flowing water in the same way as living bacteria. Results showed that while the composition of bacterial and fungal communities in the soil vary from year to year, adding manure with and without antibiotics had both caused different and consistent changes on the composition of bacterial communities. There were also higher concentrations of ARGs in soil that had manure added, however antibiotics in the manure did not cause ARGs to increase further, suggesting that even antibiotic-free manure can impact the spread of antibiotic resistance. Experimental work also demonstrated that the soil type and water content of soil can alter how bacteria and fungi respond to antibiotics in manure. The composition of bacterial and fungal communities, their activity rates, and the amount of nitrogen – an important plant nutrient with availability that is strongly affected by microbial activity – all differed with soil type and water content. Thus, while antibiotic resistance antibiotic resistance can cause measurable changes in soil across a range of environmental conditions, it is also likely to persist and spread in different ways in different environments. Finally, when water containing elements of AMR was added to soil, ARB were shown to both move through the soil easily and remain near the top of soil. In contrast, ARGs contained on genetic material outside of living cells did not move through the soil and were broken down within a few days, suggesting that antibiotic resistance likely spreads through living bacteria more than genes outside of cells. Overall, this work highlights the complexity of understanding the role of environmental transmission in the antibiotic resistance crisis and demonstrates the need for nuanced management approaches that take specific environments and conditions into account.

Gene orf18, which is situated in the conjugative transposon Tn916 from the bacterial pathogen Enterococcus faecalis, encodes a putative ArdA (alleviation of restriction of DNA) protein. ArdA from Tn916 may be responsible for the apparent immunity of the transposon to DNA restriction and modification (R/M) systems and for ensuring that the transposon has a broad host range. The orf18 gene was engineered for overexpression in Escherichia coli and the recombinant ArdA protein was purified to homogeneity. Biophysical characterisation of ArdA demonstrated tight association between ArdA and the M.EcoKI. Also, ArdA was shown to efficiently inhibit restriction and modification by all four major classes of Type I R/M enzymes in vivo. Thus, ArdA can overcome the restriction barrier following conjugation and so helps to increase the spread of antibiotic resistance genes by horizontal gene transfer. The amino acid sequence of KlcA, from the incompatibility plasmid pBP136 from Bordetella pertussis, showed a high degree of similarity with the antirestriction protein ArdB from the IncN plasmid pKM101. In this study the solution structure of KlcA was solved with high-resolution NMR and its antirestriction function demonstrated. The structure of KlcA showed a rigid globular molecule with a novel fold. No antimodification function was observed for KlcA in vivo and the antirestriction function of KlcA has been successfully shown in vivo but not in vitro. Because no direct binding of KlcA to EcoKI was observed in vitro, the mechanism of the endonuclease blocking was assumed to be different from that of ArdA. Preliminary experiments including coimmunoprecipitation assays were conducted in order to elucidate the antirestriction mechanism of KlcA.

Obiettivo di questo lavoro è stato valutare la diffusione di AR in differenti ceppi di S. thermophilus isolati tra il 1947 e il 2004 e provenienti da differenti ambienti, in modo da avere un chiaro andamento del fenomeno; questo è stato possibile analizzando un numero significativo di ceppi isolati in un periodo di tempo che va da prima dell'utilizzo degli antibiotici fino ai giorni nostri. L'espressione fenotipica è stata valutata con tre differenti metodi (microdiluizioni in brodo, E-test e Disk Diffusion), in accordo con gli standard NCCLS, per la determinazione delle MICs (Minimum Inhibitory Concentration, ovvero Concentrazioni Minime Inibenti). Per la valutazione genetica è stata impiegata la tecnica dei microarrays a DNA utilizzando oligonucleotidi da 50 e 60-mer, per un totale di 300, appartenenti a 10 diverse classi di antibiotici. La conferma dei risultati è stata ottenuta mediante PCR e sequenziamento. In 9 ceppi di S. thermophilus è stato possibile mettere in evidenza la presenza di almeno uno dei geni tetS ed ermB responsabili della resistenza agli antibiotici Tetraciclina e Eritromicina rispettivamente. / The aim of the present work was to assess the AR diffusion in a total of 70 different strains of Streptococcus thermophilus, collected between 1950 and 2004 and from different environments; in this way we had the possibility to obtain a clear overview of the response of these bacteria to a large variety of antibiotics, having been able to analyze a significant number of different strains, originated from different areas and distributed over a wide time period, since before the use of antibiotics up to the present day. The phenotypic expression has been evaluated by using three different methods: microdilution, E-test and disk diffusion. The genetic analysis was performed using 50 and 60-mer oligonucleotides DNA based micro array for the identification of AR genes; the AR genes represented by the oligonucleotides on the micro array belong to: Aminoglycoside, Extended Spectrum ?-lactamase (ESBL), Chloramphenicol, Macrolide Lincosamides and Streptogramin (MLS) group, Sulfonamide, Tetracycline, Trimethoprim and Vancomycin. tetS and ermB genes were found and sequenced in 4 out of the total of the S. thermophilus investigated. Furthermore we have wanted to establish the genetic location of above-mentioned genes and assess their transfer intra and inter species adopting the conjugation technique in plate.