Gram Negative Bacterial Diversity and Antimicrobial Resistance Profiles in Heavily Polluted Environmental Samples Around the Sır Dam Lake (Turkey)

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Gram Negative Bacterial Diversity and Antimicrobial Resistance Profiles in Heavily Polluted Environmental Samples Around the Sır Dam Lake (Turkey) Microbiology Research Journal International 19(5): 1-10, 2017; Article no.MRJI.32773 Previously known as British Microbiology Research Journal ISSN: 2231-0886, NLM ID: 101608140 SCIENCEDOMAIN international www.sciencedomain.org Gram Negative Bacterial Diversity and Antimicrobial Resistance Profiles in Heavily Polluted Environmental Samples around The Sır Dam Lake (Turkey) Emel B. Buyukunal 1* and Sevcihan Tas 1 1Department of Biology, Faculty of Science and Letters, Kahramanmaras Sutcu Imam University, Turkey. Authors’ contributions This work was carried out in collaboration between both authors. Author EBB designed the study, performed the molecular analyses, analyzed the results, drafted and revised the manuscript. Author ST collected the samples, performed the other laboratory studies. Both authors read and approved the final manuscript. Article Information DOI: 10.9734/MRJI/2017/32773 Editor(s): (1) Giuseppe Blaiotta, Department of Food Science, Via Università, Italy. Reviewers: (1) Joseph Odey Oko, Nigerian Institute of Leather and Science Technology, Zaria, Nigeria. (2) Vanessa Ochi Agostini, Oceanography Institute of Federal University of Rio Grande, Brazil. (3) Arif Tasleem, Yeungnam University, Republic of Korea. Complete Peer review History: http://www.sciencedomain.org/review-history/18765 Received 15 th March 2017 Accepted 19 th April 2017 Original Research Article th Published 24 April 2017 ABSTRACT Background: The Sır Dam Lake is located on the Ceyhan River and provides a major water-supply to agricultural fields in Southern Turkey. However, it has so far received various industrial and household wastes in excessive amounts. Aims: This study aims to analyze Gram negative bacterial diversity and antimicrobial resistance profiles in polluted environmental samples (soil, sludge, water) collected around the Dam Lake. Study Design: Gram negative bacteria were isolated from 15 polluted environmental samples and identified using both phenotypic and molecular methods. In addition, antimicrobial resistance profiles of the strains were determined by disk diffusion method. Place and Duration of Study: Environmental samples were collected from 15 different locations in Avsar region located around the Sır Dam Lake in March 2014. _____________________________________________________________________________________________________ *Corresponding author: E-mail: [email protected]; Buyukunal and Tas; MRJI, 19(5): 1-10, 2017; Article no.MRJI.32773 Methodology: Gram negative bacterial strains were identified based on biochemical tests. Biochemical identification of the bacterial isolates was further verified using CHROMagar ECC (France). A fragment corresponding to 16S rRNA gene was amplified using universal primers. The sequence analyses of amplified fragments were used for molecular identification of unidentified isolates by biochemical tests. Antimicrobial susceptibilities of the isolates were determined with disk diffusion method. Results: A total of 17 identified strains were grouped as Escherichia coli (n=8), non-fermenters (n=5) and Enterobacteriaceae (n=4). Only two strains ( Klebsiella oxytoca and Enterobacter spp.) were identified from Enterobacteriaceae . Acidovorax temperans emerged as the second predominant bacteria following to E. coli and did not display significant resistance to the tested antimicrobials. However, most of E. coli isolates as well as a single K. oxytoca and a single Acinetobacter spp. isolates displayed higher multiple antimicrobial resistance (MAR) index values that should be considered seriously for local public health. Conclusion: Gram negative bacterial distribution remarked the presence of fecal contamination. In addition, the presence of A. temperans might indicate a presence of different types of pollution, and this organism might be useful in biodegradation processes after its metabolic capability is defined. Keywords: Gram negative bacteria; Enterobacteriaceae; non-fermenters; Acidovorax temperans; antimicrobial resistance profiles. 1. INTRODUCTION surface water pollution in the upper and middle basin of the Ceyhan River was demonstrated by The Sır Dam Lake is located in the Southeastern an analysis of 13 physico-chemical parameters Turkey and mainly fed by the Ceyhan and Aksu on the surface water samples collected from 31 Rivers. The Sır Dam Lake provides an important stations around the Sır Dam Lake. The results of water-supply to several cities, including that study indicated that particular samples from Kahramanmaras, Osmaniye and Adana for three stations (Sır 2, Sır 3, and Aksu 4) near the irrigation of agricultural fields. Although the dam city of Kahramanmaras were extremely polluted − + is 35 km away from Kahramanmaras, Sır Dam by nutrients, Cl and Na due to industrial Lake is closer to Kahramanmaras (5 km). The and domestic wastewaters [1]. Microbial lake has a length of 50 km with a surface area of contamination was also proved through high 47.5 km 2 and a water capacity of 1120 hm 3. The fecal coliform counts in water samples collected essential purpose of the Sır Dam was electricity from the Aksu River [4]. Although Turkey has generation; however, the dam lake has so far around 26 river basins, most remain unstudied been an important irrigation source for [5]. Another study addressed the occurrence of agricultural fields for approximately 100.000 ha the multi-drug resistant Enterobacteria from by Iskenderun Bay. Besides, annual fish rivers in the northern Turkey and concluded that production in the lake was estimated at studied rivers could serve as reservoirs for the approximately 86 tons in 1997. Apart from antimicrobial resistance determinants in the agricultural production, many other industrial environment [6]. facilities were established around the lake. Therefore, the Sır Dam Lake has received Continuous environmental contamination by various wastes in recent years. Among these various pollutants affects native microbiota wastes, textile wastes were predominant. Other inhabiting certain environments [7]. Although this wastes include paper, leather, metal, ice-cream, negatively influences native inhabitants, it might slaughterhouses and households [1]. Although be advantageous for the adaptation of suitable the dam lake is exposed to apparent pollution organisms possessing favorable metabolic due to the rapid development of local society and features. In fact, such organisms can be useful economy, only few studies have addressed the for bioremediation purposes. Therefore, the pollution. Heavy metal pollution of the lower identification of bacterial distribution in polluted Ceyhan River basin (Adana-Turkey) was studied environments might be a crucial step for [2]. Heavy metal contamination caused by selection of bacteria with biodegradation abilities. substances such as nickel (Ni), cadmium (Cd), Although specific metabolic activities of those copper (Cu) and chromium (Cr) was also pointed bacteria is of vital importance for biodegradation out based on water samples from the Sır Dam purposes, other features such as low antibiotic Lake [3]. In addition to heavy metal pollution, resistance rates might be significant concerns for 2 Buyukunal and Tas; MRJI, 19(5): 1-10, 2017; Article no.MRJI.32773 public health since antibiotic resistant bacteria (Fig. 1). Subsequently, they were transferred into can act as a transmission tool for the emergence the sterile disposable culture tube containing 1 of new antibiotic resistant bacteria [8]. Therefore, mL of sterile 1X Phosphate Buffered Saline antibiotic resistance along with the bacterial (PBS) at pH 7.4. Buffer contained 137 mmol of diversity from polluted environments must be NaCl, 2.7 mmol g of KCl, 10 mmol of monitored to determine the risk status for Na 2HPO 4.2H 2O and 2mmol of KH 2PO 4 per L. transmission of resistance determinants from The collected samples were immediately taken to environment to humans and animals. To this the laboratory for processing and bacteriological end, the present study aims to analyze Gram analysis. negative bacterial diversity and their antimicrobial susceptibility profiles in heavily polluted 2.2 Bacteriological Analyses environmental samples (soil, sludge, water) around the Sır Dam Lake in Kahramanmaras, Bacterial inoculation was initially performed on Turkey. Eosin-Methylene Blue (EMB) agar. Afterward, inoculated plates were incubated at 35°C for 24 2. MATERIALS AND METHODS hours. Following the incubation, the plates were analyzed for selection of colonies with different 2.1 Sample Collection morphological appearances from each sample. Then, selected colonies were re-streaked on In March 2014, heavily polluted environmental fresh EMB agar for purity, and Gram-staining samples (soil, sludge, water) were collected with was performed. Gram negative pure bacterial a sterile cotton swab from 15 different locations isolates were then transferred into Tryptic Soy (37°34 ′47.09 ′′ N–36°48 ′03.84 ′′ E; 37°35 ′05.19 ′′ N– Broth (TSB) and grown at 35°C for 24 hours. 36°47 ′02.98 ′′ E) in Avsar Region around the Sır Those cultures were then used to prepare long- Dam Lake which was approximately 1 km away term bacterial stocks containing 15% of sterile from the Kahramanmaras Sutcu Imam University glycerol at the final volume [9]. Menzeret Dam Lake Ceyhan River Sır Dam Lake Kahramanmaras Sutcu Imam University Av şar Aksu River Fig. 1. The location of the Sır Dam Lake in Turkey is marked with square symbol. Sampling area was circled on the closer view of the map. GPS coordinates of the sampling area
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