The isolation of
Klebsiella and
Citrobacter, members of the
Enterobacteriaceae, from the sample sources attests to their ubiquity and makes their response to antibacterial agents relevant in public health. These organisms have been isolated from different animate (
14) and inanimate sources including sewage, refuse, sheds, and animal skins (
15-
17). In addition, they have been isolated from different parts of the human body especially the gastrointestinal tracts (
18). In some cases, they may be found in the blood system (where they cause blood sepsis), urinary, and genital tracts causing varying degrees of urinogenital disorders (
19,
20). As members of the
Enterobacteriaceae, they are considered major public health challenges (
2,
21).
The antibiotic resistance pattern of
Citrobacter and
Klebsiella spp. observed in this study revealed no significant difference between organisms isolated from HA and HN. This suggests first, the possibility of organism spillover between these 2 human groups and secondly, the independence of antibiotic resistance on the organisms’ immediate anthropogenic environment. This is in line with the concern raised by Rose et al. (2009) (
22) and Levy (2010) (
23) where drug resistant microorganisms move among people and animals, from one country to another without notice. The import of this is that the persistence and spread of antibiotic resistant bacteria in the community increases the pool of drug resistance traits. This is the condition previously known only in the traditional antibiotic-resistance hot spots of hospitals and nursing homes where close physical contact and the presence of susceptible hosts are believed to contribute to the spread of resistant bacteria.
It was observed that most of the isolated organisms were susceptible to fluroquinolone antibiotics. This is in line with reports by Malik et al. (2006) (
24) who demonstrated that fluoroquinolones have improved pharmacokinetic and pharmacodynamic properties, and are therefore more efficacious than other antibiotics. A further comparison of the resistance pattern of isolates from humans on antibiotic therapy and humans not on therapy showed that resistance to certain drugs may not necessarily be a consequence of previous exposure to the antibiotics. High correlates of > 0.5 signifies that other factors such as the discharge of antibiotic contaminated wastewater effluents (
25,
26) among others may be responsible for the resistance exhibited against the antibiotics (
Table 1). This is in line with previous researches that have adduced the presence of resistance to several factors including, but not limited to, environmental factors (
19,
27,
28), selective pressure of antibiotics (
29), genetic compatibility of microorganisms (
30), etc. Reportedly, whether or not microorganisms were previously exposed to antibiotics, their intrinsic ability to pick up genetic material from their environment (
16) is an indication that resistance could be conferred on an organism through various means (
31).
The statistical analysis of experimental findings revealed that antimicrobial resistance pattern of the organisms obtained from human and wild life correlate significantly (
Tables 3 and
4), although isolates from both sources displayed marked differences in resistance pattern against commonly used antibiotics (
Figures 3 to 6). This finding is consistent with the reports of Van den Bogaard and Stobberingh (2000) (32), Eze (2012) (
16) and Costa et al. (2013) (
31) showing that microorganisms, regardless of their source, could be resistant to antibiotics. More importantly, it further shows systematic (rather than random) variation in the mode and mechanism of resistance (
32).
The study further revealed that direct contact with antibiotics may not be the only factor contributing to and sustaining resistance. Although this stance appears debatable, some researchers have earlier shown that organisms are isolated from wildlife where there is remote chance of contact with antibiotics exhibit resistance to some test antibiotics. Multidrug-resistant bacteria have been discovered in wild birds (gulls, birds of prey) and mammals (wolves, foxes, rabbits, deer, otters) with no apparent exposure to antimicrobials (
33,
34), thus, suggesting that resistance may develop among organisms in drug pressure free environments and that once developed, resistance may not be confined to the ecological niche where it primarily originated. Since none of the ‘wildlife’ used in this research had presumably received antibiotics, it can be inferred once again that plasmid bearing and drug resistant microorganisms can be found in areas where there is no sustainable pressure for their maintenance. According to Costa et al. (2013) (
31), 2 hypothesis may justify the presence of these MDR strains of bacteria in wildlife: (i) colonization of the wildlife’s gut with resistant strains directly from the environment or harboured by their prey or, (ii) sharing of transferable genetic elements that code for resistance between “ingested” strains and the native enteric flora of wild animals. The latter takes place preferably between bacteria with the highest phylogenetic proximity, however, it may also occur between different genera and species (
31).
The possibility of antibiotic resistance mediation by genetic element was examined using plasmid profiling and electrophoretic separation of genetic components. The study revealed the occurrence of 23.1 kb plasmid DNAs in
Citrobacter and
Klebsiella (
Table 5;
Figures 5 and
6). This occurrence of 23.1 kb plasmid in these organisms is in agreement with the research reports of Dillon and Yeung (1989) (
35), Fortin et al. (1993) (
36), Van den Bogaard and Stobberingh (2000) (
37), Sharif and Astal (2004) (
38), as well as Eze (2012) (
16). This 23.1 kb plasmid has been reported to be perhaps, one of the most frequently occurring plasmids in microbes known for mediating ESBL occurrence and multiple drug resistance (
38).