Introduction
Water plays a significant role in the transmission of infectious diseases. Infections are most commonly transmitted through domestic, farm, and hospital wastewater as well as through rainwater and snowmelt. Large numbers of harmful pathogenic viruses, bacteria, protists, and parasitic worms occur in polluted waters and may pose a direct epidemiological threat to humans and animals (Michałkiewicz et al. 2011). The survival of potentially pathogenic microorganisms in a contaminated environment depends on various synergistic factors, e.g., temperature range, antagonistic interactions occurring in a given ecosystem, and individual characteristics of bacterial strains (Hawrylik 2019). Contaminated water may contain bacteria of the genus Campylobacter, which are a severe threat as they cause gastrointestinal infections in humans. In recent years, Europe has witnessed an increased incidence of campylobacteriosis in humans. In 2019, the overall prevalence of infections in the European Union was 22,682 confirmed cases (EFSA and ECDC 2021). In the European Union, campylobacteriosis is listed as a zoonosis and is subject to mandatory registration of all cases. The detection of Campylobacter spp., for example in water, should be routinely performed (Selwet 2019). Therefore, increasing efforts are being made to reduce the contamination of surface water with domestic and farm wastewater, and introduce effective water treatment methods (Górka et al. 2018). The application of ultrasounds at a frequency above 20 kHz is a highly efficient water treatment method, which is more effective than other treatment techniques (Li et al. 2019). Ultrasounds can break bacterial cell structures, usually leading to cell death. They can also selectively increase the enzymatic activity of some microorganisms (Subhedar et al. 2014; Marchesini et al. 2015). Thus far, research on the effect of ultrasound for eliminating bacterial cells from the environment has mainly focused on Escherichia coli, Salmonella typhimurium, and Listeria monocytogenes (Kumar et al. 2014). The present study aimed to determine the effectiveness of ultrasounds of low-frequency on the survival and possible elimination of Campylobacter spp. isolated from water, and to compare these results with those for reference strains.
Experimental
Materials and Methods
Water samples (n = 50) for isolating Campylobacter spp. were collected from a lake contaminated with sewage according to the procedure specified in Polish standards PN-EN ISO 5667-3:2013 (2013), and PN-EN ISO 5667-4:2003 (2003). The samples were pre-grown in Preston Broth No. 2 (product No. CM067, with lysed horse blood product No. SR0048), Preston Campylobacter Selective Supplement (product No. SR0117), and Campylobacter Growth Supplement (product No. SR0232, Oxoid) for 22–26 h at 41.5°C in an atmosphere of a gas mixture (5% O2, 10% CO2, 85% N2, CampyGen, product No. CN0025, Oxoid). Next, the samples were screened on the mCCD selective medium (product No. CM0739, Oxoid), and incubated for 40–48 h at 41.5°C in a microaerobic atmosphere. The bacterial growth on the agar was identified based on differences in colony morphology and motility examination under a microscope (Axio Imager-A2 Zeiss). The following tests were performed: oxidase (OXI detection strip, product No. 2001, Diagnostics Inc., Slovak Republic), catalase (API ID color catalase, product No. 55561, Biomérieux), and hydrolyzation of hippurate and indoxyl acetate (HIP, product No. 2006 and HIP reagent, product No. 3006; INDOXYL, product No. 2007, Diagnostics Inc.). Campylobacter spp. was also differentiated from other Gram-negative bacteria by using an O.B.I.S. Campy test (product No. ID0800M, Oxoid). Campylobacter species were identified using real-time PCR with the BAX System Real-Time PCR Assay for Campylobacter (product No. D12683449 KIT2018, Hygiena). The same procedure was used for the reference strains: Campylobacter jejuni ATCC 33291, Campylobacter coli ATCC 33559, and Campylobacter lari ATCC 35221. The standardized suspensions with turbidity corresponding to 0.5 McF in the McFarland scale (bacterial concentration 1.5 × 108/ml at an optical density of 550 nm) were prepared from the isolates obtained and reference strains. The suspensions were used to prepare a series of 10-fold dilutions (in NaCl). Next, 0.1 ml of each suspension was plated on the mCCD medium and incubated for 40–48 h at 41.5°C under a microaerobic environment. The colonies grown on plates were counted, and the counts ranged from 10 to 150 CFU (the number of replicates for each dilution was 5). Next, the effect of ultrasounds on the survival of Campylobacter was determined. For this purpose, 50 cm3 of the bacterial suspension with a density of 0.5 McF (1.5 × 108 CFU/ml) was added to 5 l of ultrapure deionized water. The bacterial suspension was placed in an Elmasonic P300H sonicator (Elma) and subjected to ultrasounds at 37 and 80 kHz for 0–30 min. Next, the samples were collected at 5-min intervals and cultured with appropriate dilutions to determine the bacterial count.
Statistical calculations were based on two factors: (1) the test was performed for two groups of microorganisms C. coli and C. coli ATCC33559, and (2) the sonication effect was assessed at six-time points: 5, 10, 15, 20, 25, and 30 min. All the combinations were carried out in triplicates with temperature measurements. The experimental design corresponded to a randomized block; hence, the one-way analysis of variance (ANOVA, α = 0.05) was used to compare the results.
Results and Discussion
Out of 50 water samples, C. coli was found in 21 samples, which was 42%. It is also noteworthy that the species diversity among the Campylobacter genus isolated from water largely depends on the sources of its contamination. According to Hokajärvi et al. (2013), C. jejuni is the commonly detected species in contaminated water. In the present study only, C. coli was isolated from the samples.
Sewage-contaminated water can show significant diversity of potentially pathogenic microorganisms. The presence of such pathogenic microbial species may entail a high epidemiological risk. E. coli is commonly considered as a primary indicator of the sanitary quality of water, sewage, and sewage precipitate (Naidoo and Olaniran 2014). For the present study, we chose the genus Campylobacter intentionally for indicating water quality. These bacteria cause campylobacteriosis, which is a zoonotic disease. They are Gram-negative, microaerophilic, motile bacilli belonging to the family Campylobacteriaceae (Rokosz et al. 2014). C. coli is one of the most common bacterial species isolated from patients with digestive system disorders (Toledo et al. 2017). For a long time, water sources were not considered as the main vector for transmission Campylobacter spp. It was widely believed that these bacteria were dormant in this environment and were referred to as VBNC (viable but not culturable) (Karkari et al. 2016). The C. coli isolated in this study and the reference C. coli ATCC 33559 strain were used for further research. Table I shows the variation in temperature and the count of C. coli and C. coli ATCC 33559, which were treated with ultrasounds generated by a continuous operation device at frequencies of 37 kHz and 80 kHz. Both the ultrasound frequencies and the duration of treatment significantly reduced the count of Campylobacter. After 5 min of treatment at 37 kHz, the number of C. coli decreased by 5.78%, whereas the temperature increased slightly, i.e., by 3°C. During the sonication process, the number of C. coli decreased by 22.22% within the 10th minute of the process. At 30 min of the experiment, the number of bacteria decreased by 40.15%. Throughout the measurement period, the temperature reached a maximum of 36°C, whereas the initial temperature was 20°C. The reference strain demonstrated a similar sequence of variation in the bacterial count and temperature values. The treatment with 80 kHz frequency showed that after 5 min of sonication, the count of C. coli decreased by 6.27%, whereas the temperature increased by 6°C. At the 10th min of the process, the bacterial count decreased by 30.07%. After 30 min of sonication, the number of C. coli decreased by 55.10%. The temperature range during the entire process increased to 39°C, whereas the initial temperature was 21°C. For the reference strain, similar values of variation were noted in the bacterial count and temperature. Ultrasounds at both frequencies 37 kHz and 80 kHz caused significant changes in the count (log CFU/ml) of C. coli isolates and the reference strain at the 10th minute of operation of the sonicator. An important finding is that the frequency of 80 kHz reduced the bacterial count from 6.86 log CFU/ml to 3.08 log CFU/ml,whereas the frequency of 37 kHz reduced the bacterial count from 6.75 log CFU/ml to 4.04 log CFU/ml. Despite significant differences in bacterial numbers after treatments with the selected ultrasound frequencies, the percentage of dead bacterial cells was similar.
Table I
Influence of the sonication process on temperature changes and the number of Campylobacter coli [log CFU/ml].
| Time [min] | 37 kHz | 80 kHz | ||||||||
|---|---|---|---|---|---|---|---|---|---|---|
| C. coli | SD | C. coli ATCC 33559 | SD | Temperature [°C] | C. coli | SD | C. coli ATCC 33559 | SD | Temperature [°C] | |
| 0 | 6.75 | ± 0.7 | 6.78 | ± 1.0 | 20 | 6.86 | ± 0.9 | 6.83 | ± 1.0 | 21 |
| 5 | 6.36 | ± 0.5 | 6.38 | ± 0.8 | 23 | 6.43 | ± 0.6 | 6.38 | ± 0.8 | 27 |
| 10 | 5.25 | ± 0.5 | 5.18 | ± 0.4 | 24 | 4.18 | ± 0.5 | 4.11 | ± 0.4 | 31 |
| 15 | 5.00 | ± 0.4 | 5.04 | ± 0.7 | 28 | 3.95 | ± 0.7 | 3.84 | ± 0.5 | 33 |
| 20 | 4.90 | ± 0.6 | 4.84 | ± 0.6 | 30 | 3.84 | ± 0.7 | 3.60 | ± 0.4 | 36 |
| 25 | 4.48 | ± 0.4 | 4.30 | ± 0.5 | 34 | 3.48 | ± 0.4 | 3.00 | ± 0.3 | 37 |
| 30 | 4.04 | ± 0.3 | 3.95 | ± 0.4 | 36 | 3.08 | ± 0.5 | 2.48 | ± 0.5 | 39 |