ANTIBIOTIC RESISTANCE PROFILE OF BACTERIA ISOLATED FROM VARIOUS SOIL SAMPLES
HTML Full TextANTIBIOTIC RESISTANCE PROFILE OF BACTERIA ISOLATED FROM VARIOUS SOIL SAMPLES
Abhik Si and Sanchita Bandyopadhyay *
Paramedical College, Durgapur, West Bengal, India.
ABSTRACT: Soil represents a major reservoir of diverse microorganisms, including bacteria capable of developing resistance to antibiotics. The present study aimed to isolate and characterize bacteria from soil samples collected from different locations in Durgapur, West Bengal, India, and to evaluate their antibiotic resistance patterns. Ten soil samples were collected and bacterial isolates were obtained using standard microbiological techniques. The isolates were characterized by colony morphology, Gram staining and biochemical tests, and their antibiotic susceptibility was determined by the Kirby–Bauer disc diffusion method following CLSI guidelines. The results revealed the presence of both Gram-positive and Gram-negative bacteria, including Staphylococcus, Micrococcus, Bacillus, Proteus, Pseudomonas and Alcaligenes species. Several isolates showed resistance to one or more antibiotics, and multiple antibiotic resistance (MAR) indices ranged from 0.4 to 1.0. The findings suggest that soil environments may act as reservoirs of antibiotic-resistant bacteria. However, species identification in the present study was based on phenotypic characteristics and should be considered presumptive. Further molecular characterization is required to confirm the identity of the isolates.
Keywords: Soil, Bacteria, Antibiotics, Antibiotic resistance, MAR index
INTRODUCTION: A broad range of microorganisms are present in soil. Since ancient times, soil bacteria play an important role on crop growth and yield by genetic transformation naturally. But the continuous use of chemical fertilizers reduces their number and proper environment for multiplication. Soil microorganisms are increasingly becoming an important source in the search for industrially important molecules 1.
In India, however, adequate information is available about the prevalence of microorganism strains in various parts of the country. In soil 80 to 99% of microorganisms remain unidentified whereas these biological communities are known to play a dominant role in maintaining a sustainable biosphere 2. Antibiotic resistance (AR) is a global problem especially in the developing countries, it also threatens public health in both developed and developing countries.
The bacterial antibiotic resistance has been reported as one of the most serious threats to the human as well as environmental health of this time, though antibiotics had tackled in the past many critical situations in clinical practices 3, 4. The rapid global emergence of resistant bacteria threatens the efficacy of antibiotics, which have revolutionized medicine and saved countless lives 5-10. Decades after antibiotics revolutionized healthcare, bacterial infections are once again an approaching threat 11. This emphasizes the urgent need to address antibiotic resistance. Different mechanisms or their combination are used by bacteria in developing resistance to antibiotics; however, a particular mechanism may be dominant and can be identifiable 12. Antibiotic resistance can be reduced but not stopped since bacteria evolve. The high rates of antimicrobial resistance occurrence have attracted the attention of international bodies such as the World Health Organization (WHO), Food and Agriculture Organization (FAO) and the World Organization for Animal Health who have now united to combat it as a common force 13. It is estimated that worldwide, 700,000 patients die annually as a result of resistant infections and if nothing is done to combat antimicrobial resistance, the death rate is estimated to escalate to 10 million by the year 2050 14. Hence the present study has been taken up where we have analysed the prevalence of potential pathogenic bacteria from the soil sample in Durgapur, West Bengal region and to determine the antibiotic resistance profiles of the isolated bacteria.
MATERIALS AND METHODS: While conducting the present study, n = 10 samples were collected from different regions of Durgapur, West Bengal, India during January–February 2025. The sampling sites included areas representing different environmental conditions such as agricultural land, roadside soil, garden soil, residential areas and open fields. The selection of multiple locations was intended to represent different environmental niches of Durgapur city in order to assess the diversity of soil bacteria and their antibiotic resistance profiles. All soil sampling procedures were performed using aseptic techniques. At each location, soil samples were collected from a depth of 5–10 cm below the surface using a sterile spatula to avoid surface contamination. Approximately 4 g of soil from each site was transferred into sterile polythene bags and transported to the laboratory in ice boxes for microbiological analysis. As a precautionary control, sterile blank samples (sterile swabs exposed to the sampling environment and processed similarly in the laboratory) were included to monitor possible contamination during sampling and handling. No microbial growth was observed in these control samples.
The moisture content and the pH of all the soil samples were determined. Furthermore soil samples were inoculated using appropriate culture media, including nutrient agar, Tryptic Soy broth with 5% yeast extract and GYM medium for obtaining bacterial isolates. After serial dilution in sterile normal saline and vortexing, the aliquots (100 µL) from each dilution were spread on the media and incubated overnight at 37 °C. This incubation temperature was selected to facilitate the growth of mesophilic bacteria including potential human-associated microorganisms, which were of particular interest in the present study due to their possible clinical relevance. However, it is acknowledged that incubation at 37 °C may preferentially select mesophilic organisms and may under-represent soil bacteria that grow optimally at lower temperatures (25–30 °C). After incubation, multiple colonies (approximately 5–10 colonies per plate) showing distinct morphological characteristics were observed. From these, colonies displaying clearly different morphological features (size, shape, colour, margin and elevation) were selected for preliminary screening. To simplify comparative antibiotic resistance analysis, one representative morphologically distinct isolate from each soil sample was selected for further characterization and antibiotic susceptibility testing. The isolated bacterial cultures were purified by streaking on Mueller-Hinton agar plates. For short-term maintenance, the isolates were preserved on cystinetryptone agar slants and stored at 4 °C. For long-term preservation, bacterial cultures were maintained as 20 % glycerol stocks at −80 °C, which ensures genetic stability of the isolates for subsequent analysis.
The isolated bacteria were characterized following phenotypic techniques (colony morphology study, gram-staining and a range of biochemical tests including indole production, methyl red, Voges–Proskauer, citrate utilization, catalase, oxidase, cellulose degradation, triple sugar iron, nitrate reduction, gelatin hydrolysis , casein hydrolysis test and sugar fermentation) for identification, according to Halt 15 and Forbes., et al. 16. These tests help to identify and differentiate bacterial species based on their metabolic properties.
These identifications should be considered presumptive, as molecular confirmation such as 16S rRNA gene sequencing was not performed in the present study. Antibiotic susceptibility testing of the isolates was performed using the Kirby–Bauer disc diffusion method on Mueller–Hinton agar plates following the guidelines of the Clinical and Laboratory Standards Institute (CLSI). Bacterial inoculum was prepared from fresh cultures and adjusted to 0.5 McFarland turbidity standard (approximately 1.5 × 10⁸ CFU/mL). The standardized inoculum was evenly spread onto Mueller–Hinton agar plates of approximately 4 mm depth using a sterile swab. In the present study, a set of commonly used antibiotics (ampicillin, chloramphenicol, gentamicin, methicillin and piperacillin) was selected in order to obtain a preliminary screening of resistance patterns among environmental bacterial isolates.
Antibiotic discs (Hi-Media, India) containing ampicillin (10 µg), chloramphenicol (30 µg), gentamicin (10 µg), methicillin (5 µg) and piperacillin (100 µg) were placed on the inoculated plates 17. Methicillin was included as a β-lactam resistance indicator, although current CLSI guidelines recommend cefoxitin as a surrogate marker for mecA-mediated methicillin resistance in Staphylococcus aureus. Piperacillin was included in the antibiotic panel as a representative broad-spectrum β-lactam antibiotic for evaluating resistance patterns among environmental isolates. Although piperacillin–tazobactam combinations are commonly used in clinical susceptibility testing, piperacillin alone was selected in this study to obtain a preliminary assessment of β-lactam resistance among soil bacteria. The plates were incubated at 37 °C for 18–24 hours, after which the zones of inhibition were measured in millimeters and interpreted according to CLSI guidelines 18. Quality control of the antibiotic susceptibility testing was performed using standard reference strains such as Escherichia coli ATCC 25922 and Staphylococcus aureus ATCC 25923, and the obtained zone diameter values were found to be within the acceptable CLSI ranges.
The MAR indices for the isolated soil bacteria were calculated and the results were explained following the criteria of Krumperman 19. The antibiotic resistance phenotypes were determined, for the isolates and the isolates with resistance to ≥ 3 test antibiotics expressed multiple antibiotic resistance phenotypes 20.
In the present study, the selected antibiotics were applied uniformly across all isolates to provide a comparative overview of resistance patterns in environmental bacteria. However, it is recognized that certain antibiotic–organism combinations (for example, β-lactams tested against non-fermenting Gram-negative rods such as Pseudomonas species) may not correspond to standard clinical testing panels.
RESULTS AND DISCUSSION: Increased and unwise use of antibiotics accelerates the emergence of multiple antibiotic resistant (MAR) bacteria, which restricts the efficacies of the currently available antibiotics in curing bacterial infections of different human ailments worldwide. Obviously, the antibiotic resistances are not limited in clinical settings, rather reported in agricultural as well as various environmental settings and foods 19, 20. The bacterial isolates obtained in the present study were recovered from soils collected from different environments within the Durgapur region, including residential areas, roadside soils and agricultural locations. These environments are frequently exposed to anthropogenic activities such as disposal of domestic waste, agricultural use of fertilizers and antibiotics, and industrial emissions. Such environmental conditions may contribute to the selection and persistence of antibiotic-resistant microorganisms in soil ecosystems.
The moisture content and the pH of all the soil samples were depicted in Table 1. A total of 10 soil bacteria isolated from the sample S1, S2, S3, S4, S5, S6, S7, S8, S9 and S10 respectively displayed varied morphological features of their colonies developed on nutrient agar plates Table 2. Among the isolated bacteria Table 3, 4 were gram negative rods (n=4; S5, S7, S8 and S9) and the other 6 isolates were either gram-positive cocci (n=5; S1, S2, S4, S6, S10) or gram-positive rods (n=1; S3). The biochemical and sugar fermentation test results of the isolated bacteria have been represented in Table 4 and Table 5. The presumptive identities of the isolated bacteria based on phenotypic and biochemical characterization are presented in Table 6.
TABLE 1: SOIL PHYSICOCHEMICAL PROPERTIES
| Sample | pH | Moisture (%) |
| S1 | 6.8 | 12 |
| S2 | 7.1 | 10 |
| S3 | 6.5 | 15 |
| S4 | 7.2 | 11 |
| S5 | 6.9 | 13 |
| S6 | 7.0 | 12 |
| S7 | 6.7 | 14 |
| S8 | 6.8 | 11 |
| S9 | 7.3 | 9 |
| S10 | 6.6 | 13 |
TABLE 2: COLONY CHARACTERISTICS OF BACTERIA ISOLATED FROM SOIL SAMPLES
| Sl. no. | Isolate | Form | Size | Elevation | Colour | Margin | Surface | Opacity | Organism |
| 1 | S1 | Circular | Small | Raised | Cream | Entire | Smooth | Opaque | Staphylococcus sp. |
| 2 | S2 | Circular | Small | Flat | Yellow | Entire | Smooth | Opaque | Micrococcus sp. |
| 3 | S3 | Circular | Small | Raised | White | Entire | Smooth | Opaque | Bacillus sp. |
| 4 | S4 | Circular | Small | Flat | Cream | Entire | Smooth | Opaque | Streptococcus sp. |
| 5 | S5 | Irregular | Small | Raised | Cream | Serrate | Smooth | Opaque | Proteus sp. |
| 6 | S6 | Circular | Small | Raised | Cream | Entire | Smooth | Opaque | Staphylococcus sp |
| 7 | S7 | Circular | Small | Raised | Light green | Entire | Wrinkled | Opaque | Pseudomonas sp. |
| 8 | S8 | Irregular | Small | Raised | Cream | Serrate | Smooth | Opaque | Proteus sp. |
| 9 | S9 | Irregular | Small | Raised | White | Entire | Smooth | Opaque | Alcaligenes sp. |
| 10 | S10 | Circular | Small | Flat | Yellow | Entire | Smooth | Opaque | Micrococcus sp. |
TABLE 3: GRAM STAINING PROPERTY OF BACTERIA ISOLATED FROM SOIL SAMPLES
| Sl. no. | Isolate | Gram stain | Shape |
| 1 | S1 | Gram positive | Cocci in cluster |
| 2 | S2 | Gram positive | Cocci in irregular cluster |
| 3 | S3 | Gram positive | Rod shaped single cell or in pair |
| 4 | S4 | Gram positive | Cocci existing in pairs and chains |
| 5 | S5 | Gram Negative | Rod shaped |
| 6 | S6 | Gram positive | Cocci in cluster |
| 7 | S7 | Gram Negative | Rod shaped |
| 8 | S8 | Gram Negative | Rod shaped |
| 9 | S9 | Gram Negative | Rod shaped |
| 10 | S10 | Gram positive | Cocci in irregular cluster |
TABLE 4: BIOCHEMICAL TEST RESULTS FOR BACTERIA ISOLATED FROM SOIL SAMPLE
| Strain code | TSI | Citrate | Indole | Catalase | Oxidase | MR | VP | DNase |
| S1 | Y/Y | - | - | + | - | - | + | + |
| S2 | Y/Y | - | - | + | + | - | - | - |
| S3 | Y/Y | + | - | + | - | - | + | - |
| S4 | Y/Y | - | - | - | - | + | - | - |
| S5 | K/A | + | + | + | - | + | - | - |
| S6 | Y/Y | - | - | + | - | - | + | + |
| S7 | K/K | + | - | + | + | - | - | - |
| S8 | K/A | + | + | + | - | + | - | - |
| S9 | K/K | + | - | + | + | - | - | - |
| S10 | Y/Y | - | - | + | + | - | - | - |
MR: Methyl red; VP: Voges-Proskauer;TSI: Triple sugar iron, P: Pink; Y: Yellow; -: Negative;+ : Positive.
TABLE 5: SUGAR FERMENTATION TEST RESULTS FOR BACTERIA ISOLATED FROM SOIL SAMPLES
| Strain Code | Sugars | ||||
| Sorbitol | Sucrose | Lactose | Maltose | Mannitol | |
| S1 | - | + | + | + | + |
| S2 | + | + | + | + | + |
| S3 | - | W | - | - | - |
| S4 | - | + | + | + | - |
| S5 | - | + | - | + | - |
| S6 | - | + | + | + | + |
| S7 | - | - | - | - | - |
| S8 | - | + | - | + | - |
| S9 | - | - | - | - | - |
| S10 | + | + | + | + | + |
W: Weakly positive; -: Negative; +: Positive.
TABLE 6: PRESUMPTIVE IDENTIFICATION OF BACTERIA ISOLATED FROM SOIL SAMPLES
| Strain Code | Bacterial identity |
| S1 | Staphylococcus aureus (presumptive) |
| S2 | Micrococcus luteus (presumptive) |
| S3 | Bacillus subtilis (presumptive) |
| S4 | Streptococcus pyogenes (presumptive) |
| S5 | Proteus vulgaris (presumptive) |
| S6 | Staphylococcus aureus (presumptive) |
| S7 | Pseudomonas aeruginosa (presumptive) |
| S8 | Proteus vulgaris (presumptive) |
| S9 | Alcaligenesfaecalis (presumptive) |
| S10 | Micrococcus luteus (presumptive) |
The zone diameters of inhibition (mm) for each isolate–antibiotic combination are presented in Table 7. These measurements were interpreted according to CLSI criteria to determine susceptibility or resistance. The antibiotic resistance profiles observed are depicted in Table 8 for the isolated gram-negative and gram-positive bacteria. Modern CLSI guidelines recommend the use of cefoxitin disc diffusion for detection of methicillin resistance in Staphylococcus aureus. In the present study methicillin discs were used as a preliminary indicator of β-lactam resistance, which represents a limitation of the methodology. In clinical microbiology laboratories, β-lactam/β-lactamase inhibitor combinations such as piperacillin–tazobactam are frequently used for susceptibility testing. However, the present study employed piperacillin alone as part of a simplified antibiotic panel for environmental screening.
Soil is widely recognized as a reservoir of microbial contaminants including antibiotic resistance genes (ARGs) and human bacterial pathogens. The antibiotic susceptibility test results, in terms of ZDIs, for the bacteria isolated from soil samples of Durgapur. The antibiotic resistance phenotypes and the MAR indices of the isolated bacteria are represented in Table 8.
TABLE 7: ZONE DIAMETER OF INHIBITION (MM) FOR ANTIBIOTIC SUSCEPTIBILITY TESTING
| Isolate | AMP (mm) | C (mm) | GEN (mm) | MET (mm) | PI (mm) |
| S1 | 10 | 11 | 22 | 9 | 12 |
| S2 | 9 | 20 | 21 | 10 | 19 |
| S3 | 11 | 22 | 23 | 10 | 12 |
| S4 | 20 | 19 | 12 | 11 | 20 |
| S5 | 18 | 20 | 22 | 10 | 11 |
| S6 | 10 | 12 | 21 | 9 | 10 |
| S7 | 11 | 12 | 20 | 10 | 18 |
| S8 | 19 | 21 | 23 | 11 | 10 |
| S9 | 8 | 9 | 10 | 8 | 9 |
| S10 | 10 | 21 | 22 | 9 | 20 |
TABLE 8: ANTIBIOTIC RESISTANCE PROFILES AND MAR INDICES FOR THE ISOLATED SOIL BACTERIA (N=10)
| Isolated Bacteria | Antibiotic resistance profile | MAR index | ||||
| AMP | C | GEN | MET | PI | ||
| Staphylococcus aureus S1 | R | R | S | R | R | 0.8 |
| Micrococcus luteus S2 | R | S | S | R | S | 0.4 |
| Bacillus subtilis S3 | R | S | S | R | R | 0.6 |
| Streptococcus pyogenes S4 | S | S | R | R | S | 0.4 |
| Proteus vulgaris S5 | S | S | S | R | R | 0.4 |
| Staphylococcus aureus S6 | R | R | S | R | R | 0.8 |
| Pseudomonas aeruginosa S7 | R | R | S | R | S | 0.6 |
| Proteus vulgaris S8 | S | S | S | R | R | 0.4 |
| Alcaligenesfaecalis S9 | R | R | R | R | R | 1 |
| Micrococcus luteus S10 | R | S | S | R | S | 0.4 |
AMP: ampicillin; C: chloramphenicol; GEN: gentamicin; MET:methicillin; PI: piperacillin.
The bacterial isolates, in the current study, showed resistance to one or more antibiotic tested; the lowest resistance to two tested antibiotics (MAR index: 0.4) was recorded for Micrococcus luteus, Streptococcus pyogenes and Proteus vulgaris strain while the highest resistance to all the five antibiotics (MAR index: 1) was displayed by Alcaligenes faecalis strain. Among 10 isolated bacteria, 5 displayed lowest mar indices of 0.4 with resistance to two antibiotics and 1 displayed highest mar index of 1 with resistance to all five antibiotics. In between 2 displayed mar indices of 0.6 and 0.8 with resistance to three and four antibiotics respectively. No intermediate susceptibility results were observed for the tested isolates. The MAR index values obtained in the present study provide a preliminary indication of resistance patterns among the tested isolates. However, since the index was calculated using a limited panel of five antibiotics, it cannot fully represent the complexity of environmental antibiotic resistomes. Comprehensive analysis involving a larger antibiotic panel and molecular characterization would be required for a more robust assessment.
Some of the bacterial species identified in the present study are commonly associated with clinical environments. Since, identification was based on phenotypic and biochemical characteristics, the bacterial species reported in the present study should be considered presumptive identifications, and further molecular confirmation (e.g., 16S rRNA gene sequencing) would be required for definitive species-level identification.
It is acknowledged that CLSI provides organism-specific antibiotic panels and testing conditions. Some antibiotic–organism combinations evaluated in the present study are not routinely included in clinical susceptibility testing panels. These combinations were included to obtain a general overview of resistance trends among environmental isolates and therefore the results of the present study should be interpreted primarily as comparative resistance screening rather than definitive clinical susceptibility profiling. Since, the same antibiotic panel was applied to all isolates, some organism–antibiotic combinations may not fully correspond to organism-specific CLSI recommendations.
CONCLUSION: The present study demonstrates the presence of diverse bacterial populations in soils from different locations in the Durgapur region. The soil sample of the current study supported the growth of gram-positive and gram –negative bacteria. Gram –positive bacteria are cocci and rod whereas gram-negative bacteria are mainly rod. The isolated bacteria showed phenotypic similarity to bacterial genera that are known to include clinically relevant species. However, the present study did not evaluate virulence factors or pathogenic potential, and therefore no definitive conclusions regarding pathogenicity can be drawn. The isolated presumptive bacteria possessed varied antibiotic resistances and MAR indices. These findings provide baseline information on soil microbial diversity and antibiotic susceptibility patterns in the region. Future studies incorporating molecular identification methods and broader environmental sampling are needed to better understand the ecological and public health implications of soil microbial communities. Therefore it is very much important to examine such environmental bacteria for different clinical relevance and to prepare effective guidelines for judicious use of antibiotics to intercept the bacterial multiple antibiotic resistances.
ACKNOWLEDGEMENTS: The authors would like to thank Dr. B. C. Roy College of Pharmacy & Allied Health Sciences and Paramedical College Durgapur for providing the necessary facilities and laboratory resources to carry out this research.
CONFLICTS OF INTEREST: The authors confirm that there is no conflict of interest related to the manuscript. The authors declare that they have no financial or non-financial conflict of interest regarding the authorship and publication of this article.
REFERENCES:
- Alexander M: Introduction to Soil Microbiology. 2nd ed. New York: John Wiley and Sons Inc 1997.
- Saha A and Santra SC: Isolation and characterization of bacteria isolated from municipal solid waste for production of industrial enzymes and waste degradation. J Microbiol Exp 2014; 1(1).
- Taneja N, Sharma M and Sharma S: Antimicrobial resistance in the environment: the Indian scenario. Indian J Med Res 2019; 149: 119–128.
- Van Boeckel TP, Gandra S, Ashok A, Caudron Q, Grenfell BT, Levin SA and Laxminarayan R: Global antibiotic consumption 2000 to 2010: an analysis of national pharmaceutical sales data. Lancet Infect Dis 2014; 14(8): 742–750.
- Golkar Z, Bagazra O and Pace DG: Bacteriophage therapy: a potential solution for the antibiotic resistance crisis. J Infect Dev Ctries 2014; 8(2): 129–136.
- Gould IM and Bal AM: New antibiotic agents in the pipeline and how they can overcome microbial resistance. Virulence 2013; 4(2): 185–191.
- Wright GD: Something new: revisiting natural products in antibiotic drug discovery. Can J Microbiol 2014; 60(3): 147–154.
- Sengupta S, Chattopadhyay MK and Grossart HP: The multifaceted roles of antibiotics and antibiotic resistance in nature. Front Microbiol 2013; 4: 47.
- Centers for Disease Control and Prevention: Antibiotic resistance threats in the United States, 2013. Available from: http://www.cdc.gov/drugresistance/threat-report-2013 (Accessed on 10 Jan 2026).
- Congressional Research Service: Life expectancy in the United States. 2005. Available from: http://www.cnie.org/nle/crsreports/05mar/RL32792.pdf (Accessed on 10 Jan 2026).
- Spellberg B and Gilbert DN: The future of antibiotics and resistance: a tribute to a career of leadership by John Bartlett. Clin Infect Dis 2014; 59(2): 71–75.
- Schweizer HP: Efflux as a mechanism of resistance to antimicrobials in Pseudomonas aeruginosa and related bacteria: unanswered questions. Genet Mol Res 2003; 2(1): 48–62.
- Maron DF: Superbug explosion triggers UN General Assembly meeting. Scientific American2016. Available from: https://www.scientificamerican.com/article/superbug-explosion-triggers-u-n-general-assembly-meeting/ (Accessed on 10 Jan 2026).
- O’Neill J: Tackling Drug-Resistant Infections Globally: Final Report and Recommendations. Review on Antimicrobial Resistance. London: Wellcome Trust and UK Government 2016.
- Holt JG: Bergey’s Manual of Systematic Bacteriology. Baltimore: Williams and Wilkins 1984.
- Forbes BA, Sahm DF and Weissfeld AS: Bailey and Scott’s Diagnostic Microbiology. 12th ed. St. Louis: Mosby (Elsevier) 2007.
- Bauer AW, Kirby WMM, Sherris JC and Turck M: Antibiotic susceptibility testing by a standardized single disk method. Am J Clin Pathol 1966; 45(4): 493–496.
- Clinical and Laboratory Standards Institute: Performance Standards for Antimicrobial Susceptibility Testing. 21st Informational Supplement M100-S21. Wayne, PA: CLSI; 2011.
- Krumperman PH: Multiple antibiotic resistance indexing of Escherichia coli to identify high-risk sources of fecal contamination of foods. Appl Environ Microbiol 1983; 46(1): 165–170.
- Odonkor ST and Simpson SV: Antibiotic-resistant bacteria and resistance genes in isolates from Ghanaian drinking water sources. J Environ Public Health 2022.
How to cite this article:
Abhik SI and Bandyopadhyay S: Antibiotic resistance profile of bacteria isolated from various soil samples. Int J Pharm Sci & Res 2026; 17(7): 2209-15. doi: 10.13040/IJPSR.0975-8232.17(7).2209-15.
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