Abstract
Free-living amoebae (FLA) are cosmopolitan microorganisms known to be pathogenic to humans who often have a history of contact with contaminated water. Swimming pools and recreational waters are among the environments where the greatest human exposure to FLA occurs. This study aimed to determine the prevalence of FLA in swimming pools and recreational waters, through a systematic review and meta-analysis that included studies published between 1977 and 2022. A total of 106 studies were included and an overall prevalence of FLA in swimming pools and recreational waters of 44.34% (95% CI = 38.57–50.18) was found. Considering the studies published up to 2010 (1977–2010), between 2010 and 2015, and those published after 2010 (> 2010–2022), the prevalence was 53.09% (95% CI = 43.33–62.73) and 37.07% (95% CI = 28.87–45.66) and 45.40% (95% CI = 35.48–55.51), respectively. The highest prevalence was found in the American continent (63.99%), in Mexico (98.35%), and in indoor hot swimming pools (52.27%). The prevalence varied with the variation of FLA detection methods, morphology (57.21%), PCR (25.78%), and simultaneously morphology and PCR (43.16%). The global prevalence by genera was Vahlkampfia spp. (54.20%), Acanthamoeba spp. (33.47%), Naegleria spp. (30.95%), Hartmannella spp./Vermamoeba spp. (20.73%), Stenamoeba spp. (12.05%), and Vannella spp. (10.75%). There is considerable risk of FLA infection in swimming pools and recreational waters. Recreational water safety needs to be routinely monitored and, in case of risk, locations need to be identified with warning signs and users need to be educated. Swimming pools and artificial recreational water should be properly disinfected. Photolysis of NaOCl or NaCl in water by UV-C radiation is a promising alternative to disinfect swimming pools and artificial recreational waters.
Graphical abstract
Similar content being viewed by others
Avoid common mistakes on your manuscript.
Introduction
Free-living amoebae (FLA) are cosmopolitan and ubiquitous microorganisms widely distributed in the environment and can be opportunistic and/or pathogenic (Visvesvara et al. 2007; Bellini et al. 2022). They have been isolated from many natural and anthropogenic environmental matrices, including plants, soil, air conditioning dust, bottled mineral water, drinking water treatment and distribution system, and cooling towers (Landell et al. 2013; Maschio et al. 2015; Javanmard et al. 2017; Soares et al. 2017; Wopereis et al. 2020; Pazoki et al. 2020). They have also been isolated from contact lenses, swimming pools, and other recreational waters (Fabres et al. 2016; Bunsuwansakul et al. 2019; Santos et al. 2021; Fabros et al. 2021).
Among its representatives with importance for human health, the genera Acanthamoeba, Naegleria, and Balamuthia stand out. Acanthamoeba spp. and its abundance in water bodies seem to be favored by higher temperatures (Kang et al 2020). These protozoa can cause illnesses in healthy people, such as Acanthamoeba keratitis (AK) which primarily affects contact lens wearers, usually due to lens wear while swimming or improper lens cleaning (Dos Santos et al. 2018). In immunosuppressed individuals, it can cause granulomatous amebic encephalitis (GAE), which can be fatal (Visvesvara et al. 2007; Sarink et al. 2022). Acanthamoeba spp. have also been reported to cause skin infections (Murakawa et al. 1995; Paltiel et al. 2004). In addition, it was isolated from 26% (17/63) of critically ill patient urine samples (Santos et al. 2009); similarly, Acanthamoeba (T4) was isolated from 22% (11/50) of urine samples collected from patients with recurrent urinary tract infection (Saberi et al. 2021).
Naegleria fowleri is known as a “brain-eating amoeba” and primarily affects healthy young people using recreational waters, causing primary amoebic meningoencephalitis (PAM) (Fowler and Carter, 1965). PAM is a serious and usually fatal disease if adequate treatment is not initiated at the onset of symptoms (Król-Turmińska and Olender 2017). The rapid deterioration in the health status of patients affected by PAM, combined with the ease of being confused with bacterial meningoencephalitis (since the symptoms are similar), as well as erratic or late diagnosis, contributes to a high prevalence of deaths (> 97%) (Capewell et al. 2015; Johnson et al. 2016). Balamuthia mandrillaris and Sappinia pedatta also cause encephalitis (Gelman et al. 2001; Visvesvara et al. 2007; Cope et al. 2019); however, there are no reports of the isolation of S. diploidea/pedatta from swimming pools and recreational waters.
The FLA essentially have three forms of life, namely, the trophozoite form (with or without flagellum) and the flagellated form which are the active forms of the protozoan, in which it may feed, reproduce, and express pathogenicity, and the form of cysts (which is the form of environmental resistance). Cysts have a double-layer wall made essentially of cellulose (Garajová et al. 2019) that protects the protozoan against unfavorable conditions (e.g., food shortages, dissection, extreme pH, and temperatures) or antimicrobial agents (e.g., NaCl, chlorine, drugs, UV, heat) (Aksozek et al. 2002; Thomas et al. 2008; Chaúque and Rott 2021a, b; Chaúque et al. 2021). FLA are considered the “Trojan Horse” of the microbial world, as phylogenetically diverse microorganisms including bacteria, fungi, and viruses survive and multiply within them; these microorganisms are called amoeba-resistant microorganisms (ARM) (Greub and Raoult 2004; Scheid 2014; Delafont et al. 2016; Hubert et al. 2021; Rayamajhee et al. 2021). A wide range of pathogens of public health importance have been described as being ARM, including Legionella pneumophila, Mycobacterium leprae, Pseudomonas spp., Candida auris, and various viruses (Maschio et al. 2015; Staggemeier et al. 2016; Balczun and Scheid 2017; Turankar et al. 2019; Nisar et al. 2020; Hubert et al. 2021). The participation of FLA in the environmental persistence of severe acute respiratory syndrome 2 (SARS-CoV-2) has also been proposed (Chaúque et al. 2022; Dey et al 2022). All these aspects that characterize the profile of FLA constitute the main attributes that determine the great importance of these protozoa for human health and the environment.
Although increasingly prevalent, diseases caused by FLA remain rare; however, the presence of these protozoa, especially in the aquatic environment, is well documented (Milanez et al. 2022; Stapleton 2021; Saburi et al. 2017; Caumo et al. 2009). The presence of FLA in swimming pools and other recreational waters is of concern, as they can be pathogenic or opportunistic and/or lead to the persistence of non-amoebic pathogens in the water, including waters treated with chlorine-based disinfectants (Siddiqui and Khan 2014; Kiss et al. 2014; Dey et al. 2021). It was determined that the prevalence of Naegleria spp. in different water sources around the world (considering data from 35 countries) was 26.42%, in recreational water it was 21.27% (10.80–34.11), and in swimming pools was 44.80% (16.19–75.45) (Saberi et al. 2020); however, the global prevalence of FLA in swimming pools and recreational waters remains to be determined. The present systematic review and meta-analysis aimed to determine the prevalence of FLA in swimming pools and recreational waters worldwide.
Methods
Article search strategy
The present study, which aimed to determine the prevalence of FLA in swimming pools and recreational waters, was planned and carried out based on the PRISMA 2020 guidelines (Page et al. 2021) (Fig. 1). The search for scientific articles was performed in different databases, including Web of Science, Scopus, PubMed, ScienceDirect, EMBASE, ProQuest, and CAPES periódicos, between July 4 and 9, 2022. In these databases, articles were retrieved using a combination of the following search terms combined with appropriate Boolean operators: “Free-living amoeba,” “swimming pool,” “recreational water,” “prevalence,” “epidemiology,” and “hot springs.” The references of the selected articles were examined in search of some interesting literature. The search for articles in the database was performed by B.J.M.C, and the accuracy of the searches was verified by D.L.S.
Selection and exclusion criteria
The screening focused essentially on the title and then on the abstract of the articles. All retrieved articles written in English (reporting primary data), with accessible full text, dealing with the presence of FLA in swimming pools and human recreation waters were selected. Studies based on natural surface waters that do not clearly state that the samples were collected in places where human recreational activities certainly take place were not selected. Studies whose data were insufficient, unclear, or duplicated were excluded. Case studies that do not report the prevalence of FLA in swimming pools and human recreation waters were also excluded.
Data analysis procedure
Data were independently extracted and verified by two authors (B.J.M.C and D.L.S); data verification was performed three times. Data extracted from all articles that met the inclusion criteria were included in the calculation of the global prevalence of FLA in swimming pools and recreational waters. To calculate the prevalence of each FLA genera, only data extracted from articles that included molecular methods for the identification of FLA were used. Data analysis was performed by two authors (D.A and B.J.M.C) using Stata software (version 14; Stata Corp, College Station, TX, USA) and GraphPad prism 8.02. A random-effects model meta-analysis was performed to estimate the combined and weighted prevalence of FLA in swimming pools and recreational waters, using a 95% confidence interval, and the results are visualized using a forest plot. Cochran’s Q test (chi-square) and the Higgins I2 statistic were used to calculate the heterogeneity index among the selected studies. I2 values < 25%, 25%–50%, and > 50% meant low, moderate, and high heterogeneity, respectively. The Egger’s test was used to assess the significance of publication bias among the selected studies; P < 0.001 was considered significant.
Results
From the total of 2034 documents returned by the databases accessed, using the search strategy and inclusion criteria described above, 106 articles were selected (Table 1). These studies are distributed in a total of 30 countries, namely Iran (33), Taiwan (12), Egypt (8), Malaysia (6), Brazil (4), Italy (4), Turkey (4), USA (4), Mexico (3), Saudi Arabia (3), China (2), France (2), Philippines (2), Spain (2), and Thailand (2). One study was included from each of the following countries: Belgium, Bulgaria, Cape Verde, Chile, Finland, Germany, Hungary, India, Jamaica, Japan, Norway, Poland, Portugal, Sweden, and Switzerland. Among the studies, 74.52% (79/106) used or included molecular methods to identify FLA, while 25.47% (27/106) used only morphological methods.
The included studies were published between 1977 and 2022, and the distribution of studies by year and the average percentage value of positive samples per year are shown in Fig. 2. FLA were detected in at least 1 sample of 97.17% (103/106) of selected studies (Table 1).
Publication bias was checked by Egger’s regression test, showing that it may have a substantial impact on total prevalence estimate (Egger bias: 6.8, P < 0.001) (Fig. 3). This suggests that the reported global prevalence may have been impacted by publication bias.
Based on the random-effects model meta-analysis, the pooled prevalence of FLA in water sources was 44.34% (95% CI = 38.57–50.18). The included studies demonstrated a strong heterogeneity (Q = 2198.0, df = 102, I2 = 95.4%, P < 0.0001) (Fig. 4).
The global prevalence of FLA in swimming pools and recreational waters considering studies published up to 2010 (1977–2010) was considerably higher 53.09% (95% CI = 43.33–62.73) than in studies published between 2010 and 2015, 37.07% (95% CI = 28.87–45.66), and those published after 2015 (> 2015–2022) 45.40% (95% CI = 35.48–55.51) (Table 2).
Considering the continents covered by the selected studies, the highest prevalence 63.99% (95% CI = 45.03–80.92) was reported in America and the lowest 37.38% (95% CI = 30.12–44.93) in Asia. Among the countries from which more than one study was included, Mexico had the highest prevalence of FLA in swimming pools and recreational waters 98.35% (95% CI = 92.56–99.96), and the lowest prevalence 10.15% (95% CI = 4.99–16.87) was recorded in China (Table 2).
Considering the different sampling sources, the highest prevalence of FLA 52.27% (95% CI = 14.55–88.50) was obtained in indoor hot swimming pools, and the lowest prevalence 39.12% (95% CI = 30.48–48.13) was obtained in hot springs (Table 2).
The analysis of data from studies that used only morphological methods to identify FLA showed the highest prevalence 57.21% (95% CI = 37.99–7535), the lowest prevalence 25.78% (95% CI = 14.18–39.44) was obtained from studies based only on molecular methods (PCR), and an intermediate prevalence value 43.16% (95% CI = 37.73–48.67) was obtained by analyzing studies that simultaneously used morphological and molecular methods (Table 2).
The subgroup analysis revealed that there were statistically significant differences between the overall prevalence of FLA in water sources and year (X2 = 449.4, P < 0.001), continent (X2 = 156.7, P < 0.001), country (X2 = 26.0, P < 0.001), and diagnostic method (X2 = 373.5, P < 0.001) (Table 2).
The highest values of the global prevalence of different genera of FLA in swimming pools and recreational waters were from Vahlkampfia spp. (54.20%), Acanthamoeba spp. (33.47%), and Naegleria spp. (30.95%). For other genera, Hartmannella spp./Vermamoeba spp., Stenamoeba spp., and Vannella spp., the global prevalence values were 20,73%, 12.05%, and 10.75%, respectively (Table 3). The results of Egger’s regression test, as well as the forest plot of the worldwide prevalence of each of these FLA genera in swimming pools and recreational waters, can be seen in Fig. S1, S2, S3, S4, S5, and S6 of the supplementary material, respectively.
Discussion
FLA are cosmopolitan microorganisms ubiquitous in all matrices of natural and anthropogenic environments, including water resources. The presence of FLA in pools and recreational waters is worrying, since some of these microorganisms are human pathogens/opportunists, as well as being widely implicated in persistence and/or pseudo-resistance of pathogenic bacteria, viruses, and fungi in water, including in water treated with disinfectants (Thomas et al. 2004; Staggemeier et al. 2016; Mavridou et al. 2018; Gomes et al. 2020; Hubert et al. 2021).
The studies included in present review are distributed by five continents; however, they have a heterogeneous spatial distribution within the territories of the continents; this can suggest differences in the level of FLA importance for health in the contexts of different countries, as well as differences in the frequency of cases diseases associated with the FLA. The frequency of cases of FLA-related diseases can be influenced by the difference in the predominance of risk factors and the sensitivity of the health surveillance strategy of each country, as well as the heterogeneous distribution of trained professionals carrying out research in this area. In addition, the ease of confusing symptoms of diseases associated with the FLA with those caused by other microorganisms, combined with some cases of rapid deterioration of the patient’s health and death (Jahangéer et al. 2020) can contribute to the rarity of reports or even the lack of association of diseases with FLA, especially in contexts where post-mortem study policies are not robust.
Our findings show that the global prevalence of FLA in swimming pools and recreational waters is 44.34%; however, a higher (53.09%) and intermediate (45.40%) prevalence value was obtained when considering the data from studies published up to 2010 and studies published after 2015, respectively. A lower prevalence value (37.07%) was obtained when analyzing data from studies published between 2010 and 2015 (Table 2). A similar result was reported in a study that aimed to determine the prevalence of Naegleria spp. in water resources (Saberi et al. 2020). This reduction in the prevalence reported in most recent studies was attributed to the most accurate diagnosis and reduction of false positive results (Jahangeeer et al. 2020; Saberi et al. 2020), as contrary to studies published up to 2010, the vast majority of studies published after 2010 used molecular methods for FLA identification. Curiously, our results show that the overall prevalence of FLA considering studies that used both morphological and molecular methods is close to the mean of the prevalence values obtained from data from studies that used only one of the methods (Table 2). This may suggest that the simultaneous use of these two methods reduces the extreme values obtained separately by each of the methods, and that these methods can be complementary, especially in studies that aim to assess the presence or absence of viable FLA in water samples. The authors agree that the morphological method (generally based on culture) is more laborious and less precise than molecular methods in the identification of FLA (Saberi et al. 2020; Hikal et al. 2018).
The subgroup analysis considering the distribution of the studies by the continents showed that FLA are more prevalent in the swimming pools and recreational water from America (63.99%), followed by Europe (51.99%) and Africa (51.27%). In relation to countries, the highest value of the prevalence of FLA was obtained in Mexico (98.35%), followed by Malaysia (87.38%), France (69.62%), and Italy (64.76%), and the lowest values were obtained in China (10.15%), Taiwan (26.33%), Turkey (30.60), and Thailand (32.68%). As for the sample source, the indoor hot swimming pools presented a higher value (52.27%) of FLA prevalence, followed by public swimming pools (49.47%) and thermal swimming pools (46.05%). The genera Vahlkampfia spp., Acanthamoeba spp., and Naegleria spp. were more prevalent, presenting the following prevalence values, 54.20%, 33.47%, and 30.95%, respectively (Table 3). The lowest prevalence value was for Vannella spp. (10.75%). These results are in accordance with other authors whose studies reported high prevalence of FLA (Acanthamoeba spp. 48.5%, Naegleria spp. 46.0%, Vermamoeba spp. 4.7%, and Balamuthia spp. 0.7%) in hot springs (Fabros et al. 2021). Saberi et al. (2020) reported the following prevalence values for Naegleria spp. 44.80%, 32.88%, and 21.27%, in swimming pools, hot springs, and recreational waters, respectively. The subgroup analysis showed that prevalence values are statistically different (P < 0.001) for all variables studied (Table 2). These findings are in accordance with other studies that reported a variable distribution in abundance and diversity of FLA species around the world (Jahangéer et al. 2020; Saberi et al. 2020; Fabros et al. 2021).
The global prevalence of FLA reported in the present study (44.34%) is worrying, since direct contact between humans and these waters is often established. In addition, several studies have reported the isolation of several potentially pathogenic FLA (Caumo et al. 2009; Alves et al. 2012; Behniafar et al. 2015;) and others with proven pathogenicity in ex vivo and in vivo trials (Brown and Cursons 1977; Janitschke et al. 1980; Rivera et al. 1983, 1993; Gianinazzi et al. 2009). Most of these FLA are identified as N. fowleri, Acanthamoeba spp., and Balamuthia mandrillaris. Most isolates of Acanthamoeba spp. reported as pathogens are distributed among the T5, T11, T15, T3, and T4 genotypes, and among them, the T4 genotype is more prevalent in hot springs (Mahmoudi et al. 2015; Fabros et al. 2021) and is associated with most cases of Acanthamoeba keratitis (Diehl et al. 2021; Bellini et al. 2022). The presence and abundance of FLA in swimming pool water clearly indicate that in addition to these microorganisms being resistant to chlorine in the dosage used in the treatment of drinking water (Thomas et al. 2004; Majid et al. 2017; Gomes et al. 2020), they are also resistant to chlorine and other disinfectants in the dosage used for swimming pools and artificial recreational waters (Rivera et al. 1983; Kiss et al. 2014; Zeybek et al. 2017). Acanthamoeba castellanii trophozoites and cysts have been reported to be resistant to exposure for more than 2 h to NaOCl and NaCl at concentrations up to 8 mg/L and 40 g/L, respectively. On the other hand, exposure to the combined effect of NaOCl or NaCl with ultraviolet C (UV-C) radiation resulted in rapid inactivation of trophozoites even when lower concentrations of NaOCl and NaCl were used (Chaúque and Rott 2021a, b). Cyst inactivation was achieved by twice as long exposure (300 min) to the combined effect of NaOCl or NaCl and UV-C, with redosing of NaOCl. Despite having demonstrated that both methods are effective, and that they have a strong potential to be used in the effective disinfection of swimming pool water, it was found that the use of NaCl is more cost-effective, as it is cheaper and has a residual effect; redosing is not necessary and is simple to apply (Chaúque and Rott 2021a, b). On the other hand, the use of solar UV radiation (UV-A and B) in place of UV-C (which depends on electricity) can further reduce the cost of the disinfection process. The effectiveness of using solar UV to photolyse NaOCl to inactivate chlorine-resistant microorganisms has been previously documented (Zhou et al. 2014). Readers interested in solar water disinfection technology applicable to recreational water treatment are directed to the appropriate literature (Chaúque and Rott 2021a; Chaúque et al. 2022).
The main aspects that constituted limitations for the present study are the following: the lack of studies carried out in most countries of the world; the heterogeneous distribution of the number of studies among the included countries; difference in FLA identification methods among many studies and discrepancy in the number of samples considered positive by the morphological and molecular method in the same study. The loss of isolates from positive samples in some studies, due to fungal contamination of non-nutrient agar plates prior to molecular identification of the amoebae, was also a limitation.
Conclusion
It is concluded that the prevalence of FLA in swimming pools and recreational waters is high and, therefore, of concern, since there is a risk of contracting infection by pathogenic amoebae or other pathogens (such as fungi, bacteria, and viruses) that may be harbored and dispersed by FLA in water (Mavridou et al. 2018). Thus, it is necessary to implement disinfection techniques that are effective in eliminating microorganisms, including FLA, in swimming pools and artificial recreational waters. The use of the combined effect of NaCl and UV-C has great potential to be used to eliminate or minimize the risk of infection by FLA in swimming pools and other artificial recreational waters. The potential risk of infection by FLA in natural recreational waters needs to be routinely quantified by health surveillance. Warning signs need to be placed where there is minimal risk of infection by FLA, and people using these water bodies need to be educated about the potential risk and possible safety measures. These measures include not diving in recreational waters wearing contact lenses, preventing water from entering the airways and eyes, and avoiding jumping into the water. Health care workers (especially those working near recreational water use sites with risk of infection by FLA) need to be trained to be on the lookout for symptoms suggestive of infection by FLA, especially in summer.
Data availability
Not applicable.
References
Aksozek A, Mcclellan K, Howard K et al (2002) Resistance of Acanthamoeba castellanii cysts to physical. Chemical, and Radiological Conditions. J Parasitol 88(3):621–623. https://doi.org/10.1645/0022-3395(2002)088[0621:ROACCT]2.0.CO;2
Al-Herrawy A, Bahgat M, Mohammed AE et al (2014) Acanthamoeba species in swimming pools of Cairo, Egypt. Iran J Parasitol 9(2):194–201
Al-Herrawy AZ, Gad MA, Abd El-Aziz A et al (2016) Morphological and molecular detection of potentially pathogenic free-living amoebae in swimming pool samples. Egypt J Environ Res 5:1–13
Al-Herrawy AZ, Khalil MI, El-Sherif SS et al (2017) Surveillance and molecular identification of Acanthamoeba and Naegleria species in two swimming pools in Alexandria University, Egypt. Iran J Parasitol 12(2):196–205
Alves DSMM, Moraes AS, Nitz N et al (2012) Occurrence and characterization of Acanthamoeba similar to genotypes T4, T5, and T2/T6 isolated from environmental sources in Brasília, Federal District, Brazil. Exp Parasitol 131(2):239–244. https://doi.org/10.1016/j.exppara.2012.04.011
Armand B, Motazedian MH, Asgari Q (2016) Isolation and identification of pathogenic free-living amoeba from surface and tap water of Shiraz City using morphological and molecular methods. Parasitol Res 115(1):63–68. https://doi.org/10.1007/s00436-015-4721-7
Attariani H, Turki H, Shoja S et al (2020) Investigating the frequency of free-living amoeba in water resources with emphasis on Acanthamoeba in Bandar Abbas city, Hormozgan province, Iran in 2019–2020. BMC Res Notes 13(1):420. https://doi.org/10.1186/s13104-020-05267-z
Aykur M, Dagci H (2021) Evaluation of molecular characterization and phylogeny for quantification of Acanthamoeba and Naegleria fowleri in various water sources. Turkey Plos One 16(8):e0256659. https://doi.org/10.1371/journal.pone.0256659
Azlan AM, Rasid MN, Richard RL et al (2016) Titiwangsa Lake a source of urban parasitic contamination. Trop Biomed 33(3):594–598
Badirzadeh A, Niyyati M, Babaei Z et al (2011) Isolation of free-living amoebae from sarein hot springs in Ardebil Province, Iran. Iran J Parasitol 6(2):1–8
Bakri R, Mohamed R, Alghanmi M et al (2021) Isolation, morphotyping, molecular characterization and prevalence of free-living amoebae from different water sources in Makkah city, Saudi Arabia. J Umm Al-Qura Univ Med Sci 7(2):5–8
Balczun C, Scheid PL (2017) Free-living amoebae as hosts for and vectors of intracellular microorganisms with public health significance. Viruses 9(4):65. https://doi.org/10.3390/v9040065
Ballares LD, Masangkay FR, Dionisio J et al (2020) Molecular detection of Acanthamoeba spp. in Seven Crater Lakes of Laguna, Philippines. J Water Health 18(5):776–784. https://doi.org/10.2166/wh.2020.146
Behniafar H, Niyyati M, Lasjerdi Z (2015) Molecular characterization of pathogenic Acanthamoeba isolated from drinking and recreational water in East Azerbaijan, Northwest Iran. Environ Health Insights 9:7–12. https://doi.org/10.4137/EHI.S27811
Bellini NK, Thiemann OH, Reyes-Batlle M et al (2022) A history of over 40 years of potentially pathogenic free-living amoeba studies in Brazil - a systematic review. Mem Inst Oswaldo Cruz 117:e210373. https://doi.org/10.1590/0074-02760210373
Berrilli F, Di Cave D, Novelletto A, Di Filippo MM (2021) PCR-based identification of thermotolerant free-living amoebae in Italian hot springs. Eur J Protistol 80:125812. https://doi.org/10.1016/j.ejop.2021.125812
Bonilla-Lemus P, Rojas-Hernández S, Ramírez-Flores E et al (2020) Isolation and identification of Naegleria Species in irrigation channels for recreational use in Mexicali Valley, Mexico. Pathogens 9(10):820. https://doi.org/10.3390/pathogens9100820
Brown TJ, Cursons RT (1977) Pathogenic free-living amebae (PFLA) from frozen swimming areas in Oslo, Norway. Scand J Infect Dis 9(3):237–240. https://doi.org/10.3109/inf.1977.9.issue-3.16
Bunsuwansakul C, Mahboob T, Hounkong K et al (2019) Acanthamoeba in Southeast Asia - overview and challenges. Korean J Parasitol 57(4):341–357. https://doi.org/10.3347/kjp.2019.57.4.341
Capewell LG, Harris AM, Yoder JS et al (2015) Diagnosis; clinical course; and treatment of primary amoebic meningoencephalitis in the United States; 1937–2013. J Pediatric Infect Dis Soc 4:68–75. https://doi.org/10.1093/jpids/piu103
Caumo K, Frasson AP, Pens CJ (2009) Potentially pathogenic Acanthamoeba in swimming pools: a survey in the southern Brazilian city of Porto Alegre. Ann Trop Med Parasitol 103(6):477–485. https://doi.org/10.1179/136485909X451825
Chaúque BJM, Benetti AD, Corção G et al (2021) A new continuous-flow solar water disinfection system inactivating cysts of Acanthamoeba castellanii, and bacteria. Photochem Photobiol Sci 20(1):123–137. https://doi.org/10.1007/s43630-020-00008-4
Chaúque BJM, Brandão FG, Rott MB (2022) Development of solar water disinfection systems for large-scale public supply, state of the art, improvements and paths to the future – a systematic review. J Environ Chem Eng 10(3):107887. https://doi.org/10.1016/j.jece.2022.107887
Chaúque BJM, Rott MB (2021a) Photolysis of sodium chloride and sodium hypochlorite by ultraviolet light inactivates the trophozoites and cysts of Acanthamoeba castellanii in the water matrix. J Water Health 19(1):190–202. https://doi.org/10.2166/wh.2020.401
Chaúque BJM, Rott MB (2021b) Solar disinfection (SODIS) technologies as alternative for large-scale public drinking water supply: advances and challenges. Chemosphere 281:130754. https://doi.org/10.1016/j.chemosphere.2021.130754
Chaúque BJM, Rott MB (2022) The role of free-living amoebae in the persistence of viruses in the era of severe acute respiratory syndrome 2, should we be concerned? Rev Soc Bras Med Trop 55:e0045. https://doi.org/10.1590/0037-8682-0045-2022
Cope JR, Landa J, Nethercut H, Collier SA, Glaser C, Moser M, Puttagunta R, Yoder JS, Ali SL (2019) (2018) The Epidemiology and Clinical Features of Balamuthia mandrillaris Disease in the United States 1974–2016. Clinical Infectious Diseases 68(11):1815–1822. https://doi.org/10.1093/cid/ciy813
De Jonckheere JF (1979) Pathogenic free-living amoebae in swimming pools: survey in Belgium. Ann Microbiol (paris) 130B(2):205–212
Değerli S, Değerli N, Çamur D et al (2020) Genotyping by sequencing of Acanthamoeba and Naegleria isolates from the thermal pool distributed throughout Turkey. Acta Parasit 65:174–186. https://doi.org/10.2478/s11686-019-00148-3
Delafont V, Bouchon D, Héchard Y, Moulin L (2016) Environmental factors shaping cultured free-living amoebae and their associated bacterial community within drinking water network. Water Res 100:382–392. https://doi.org/10.1016/j.watres.2016.05.044
Dey R, Dlusskaya E, Ashbolt NJ (2022) SARS-CoV-2 surrogate (Phi6) environmental persistence within free-living amoebae. J Water Health 20(1):83–91. https://doi.org/10.2166/wh.2021.167
Dey R, Folkins MA, Ashbolt NJ (2021) Extracellular amoebal-vesicles: potential transmission vehicles for respiratory viruses. NPJ Biofilms Microbiomes 7(1):25. https://doi.org/10.1038/s41522-021-00201-y
Di Filippo MM, Novelletto A, Di Cave D, Berrilli F (2017) Identification and phylogenetic position of Naegleria spp. from geothermal springs in Italy. Exp Parasitol 183:143–149. https://doi.org/10.1016/j.exppara.2017.08.008
Diehl MLN, Paes J, Rott MB (2021) Genotype distribution of Acanthamoeba in keratitis: a systematic review. Parasitol Res 120:3051–3063. https://doi.org/10.1007/s00436-021-07261-1
Dodangeh S, Kialashaki E, Daryani A et al (2018) Isolation and molecular identification of Acanthamoeba spp. from hot springs in Mazandaran province, northern Iran. J Water Health 16(5):807–813. https://doi.org/10.2166/wh.2018.098
Dos Santos DL, Kwitko S, Marinho DR (2018) Acanthamoeba keratitis in Porto Alegre (southern Brazil): 28 cases and risk factors. Parasitol Res 117(3):747–750. https://doi.org/10.1007/s00436-017-5745-y
Eftekhari-Kenzerki R, Solhjoo K, Babaei Z (2021) High occurrence of Acanthamoeba spp. in the water samples of public swimming pools from Kerman Province, Iran. J Water Health 19(5):864–871. https://doi.org/10.2166/wh.2021.162
El-Badry AA, Aufy SM, El-Wakil ES et al (2020) First identification of Naegleria species and Vahlkampfia ciguana in Nile water, Cairo, Egypt: seasonal morphology and phylogenetic analysis. J Microbiol Immunol Infect 53(2):259–265. https://doi.org/10.1016/j.jmii.2018.06.003
Esboei BR, Fakhar M, Saberi R (2020) Genotyping and phylogenic study of Acanthamoeba isolates from human keratitis and swimming pool water samples in Iran. Parasite Epidemiol Control 11:e00164. https://doi.org/10.1016/j.parepi.2020.e00164
Evyapan G, Koltas IS, Eroglu F (2015) Genotyping of Acanthamoeba T15: the environmental strain in Turkey. Trans R Soc Trop Med Hyg 109(3):221–224. https://doi.org/10.1093/trstmh/tru179
Fabres LF, Dos Santos SPR, Benitez LB, Rott MB (2016) Isolation and identification of Acanthamoeba spp. from thermal swimming pools and spas in Southern Brazil. Acta Parasitol. 61(2):221–7. https://doi.org/10.1515/ap-2016-0031
Fabros MRL, Diesta XRS, Oronan JA et al (2021) Current report on the prevalence of free-living amoebae (FLA) in natural hot springs: a systematic review. J Water Health 19(4):563–574. https://doi.org/10.2166/wh.2021.101
Fowler M, Carter RF (1965) Acute pyogenic meningitis probably due to Acanthamoeba sp.: a preliminary report. British medical journal 2(5464):740–742. https://doi.org/10.1136/bmj.2.5464.734-a
Gabriel S, Khan NA, Siddiqui R (2019) Occurrence of free-living amoebae (Acanthamoeba, Balamuthia, Naegleria) in water samples in Peninsular Malaysia. J Water Health 17(1):160–171. https://doi.org/10.2166/wh.2018
Garajová M, Mrva M, Vaškovicová N et al (2019) Cellulose fibrils formation and organisation of cytoskeleton during encystment are essential for Acanthamoeba cyst wall architecture. Sci Rep 9:4466. https://doi.org/10.1038/s41598-019-41084-6
Gelman BB (2001) Amoebic Encephalitis Due to Sappinia diploidea. JAMA 285(19):2450. https://doi.org/10.1001/jama.285.19.2450
Ghaderifar S, Najafpoor AA, Zarrinfar H et al (2018) Isolation and identification of Acanthamoeba from pond water of parks in a tropical and subtropical region in the Middle East, and its relation with physicochemical parameters. BMC Microbiol 18(1):139. https://doi.org/10.1186/s12866-018-1301-x
Gianinazzi C, Schild M, Wüthrich F et al (2009) Potentially human pathogenic Acanthamoeba isolated from a heated indoor swimming pool in Switzerland. Exp Parasitol 121(2):180–186. https://doi.org/10.1016/j.exppara.2008.11.001
Gianinazzi C, Schild M, Zumkehr B et al (2010) Screening of Swiss hot spring resorts for potentially pathogenic free-living amoebae. Exp Parasitol 126(1):45–53. https://doi.org/10.1016/j.exppara.2009.12.008
Gogate A, Deodhar L (1985) Isolation and identification of pathogenic Naegleria fowleri (aerobia) from a swimming pool in Bombay. Trans R Soc Trop Med Hyg 79(1):134. https://doi.org/10.1016/0035-9203(85)90258-5
Gomes TS, Vaccaro L, Magnet M (2020) Presence and interaction of free-living amoebae and amoeba-resisting bacteria in water from drinking water treatment plants. Sci Total Environ 719:137080. https://doi.org/10.1016/j.scitotenv.2020.137080
Górnik K, Kuźna-Grygiel W (2004) Presence of virulent strains of amphizoic amoebae in swimming pools of the city of Szczecin. Ann Agric Environ Med 11(2):233–236
Greub G, Raoult D (2004) Microorganisms resistant to free-living amoebae. Clin Microbiol Rev 17:413–433
Haddad MHF, Khoshnood S, Mahmoudi MR et al (2019) Molecular identification of free-living amoebae (Naegleria spp., Acanthamoeba spp. and Vermamoeba spp.) isolated from un-improved hot springs, Guilan Province, Northern Iran. Iran J Parasitol 14(4):584–591
Hamadto HH, Aufy SM, el-Hayawan IA et al (1993) Study of free living amoebae in Egypt. J Egypt Soc Parasitol 23(3):631–637
Hikal WM, Hikal W, Dkhil MA, Dkhil M (2018) Nested PCR assay for the rapid detection of Naegleria fowleri from swimming pools in Egypt. Acta Ecol Sin 38:102–107. https://doi.org/10.1016/j.chnaes.2017.06.013
Hsu B-H, Ma P-H, Liou T-S (2009) Identification of 18S ribosomal DNA genotype of Acanthamoeba from hot spring recreation areas in the central range, Taiwan. J Hydrol 367(3–4):249–254. https://doi.org/10.1016/j.jhydrol.2009.01.018
Hsu BM, Lin CL, Shih FC (2009) Survey of pathogenic free-living amoebae and Legionella spp. in mud spring recreation area. Water Res 43(11):2817–28. https://doi.org/10.1016/j.watres.2009.04.002
Huang SW, Hsu BM (2010) Isolation and identification of Acanthamoeba from Taiwan spring recreation areas using culture enrichment combined with PCR. Acta Trop 115(3):282–287. https://doi.org/10.1016/j.actatropica.2010.04.012
Huang SW, Hsu BM (2010) Survey of Naegleria and its resisting bacteria-Legionella in hot spring water of Taiwan using molecular method. Parasitol Res 106:1395–1402. https://doi.org/10.1007/s00436-010-1815-0
Huang SW, Hsu BM (2011) Survey of Naegleria from Taiwan recreational waters using culture enrichment combined with PCR. Acta Trop 119(2–3):114–118. https://doi.org/10.1016/j.actatropica.2011.04.016
Hubert F, Rodier MH, Minoza A (2021) Free-living amoebae promote Candida auris survival and proliferation in water. Lett Appl Microbiol 72(1):82–89. https://doi.org/10.1111/lam.13395
Hussain RHM, Ishak AR, Ghani MKA et al (2019) Occurrence and molecular characterisation of Acanthamoeba isolated from recreational hot springs in Malaysia: evidence of pathogenic potential. J Water Health 17(5):813–825. https://doi.org/10.2166/wh.2019.214
Init I, Lau YL, Fadzlun AA, Foead AI (2010) Detection of free living amoebae, Acanthamoeba and Naegleria, in swimming pools, Malaysia. Trop Biomed 27(3):566–577
Ithoi I, Ahmad AF, Nissapatorn V et al (2011) Detection of Naegleria species in environmental samples from Peninsular Malaysia. PLoS ONE 6(9):e24327. https://doi.org/10.1371/journal.pone.0024327
Izumiyama S, Yagita K, Furushima-Shimogawara R et al (2003) Occurrence and distribution of Naegleria species in thermal waters in Japan. J Eukaryot Microbiol 50(Suppl):514–515. https://doi.org/10.1111/j.1550-7408.2003.tb00614.x
Jahangeer M, Mahmood Z, Munir NR et al (2020) Naegleria fowleri: sources of infection, pathophysiology, diagnosis, and management; a review. Clin Exp Pharmacol Physiol 47(2):199–212. https://doi.org/10.1111/1440-1681.13192
Janitschke K, Werner H, Müller G (1980) Das Vorkommen von freilebenden Amöben mit möglichen pathogenen Eigenschaften in Schwimmbädern [Examinations on the occurrence of free-living amoebae with possible pathogenic traits in swimming pools (author’s transl)]. Zentralbl Bakteriol b 170(1–2):108–122
Javanmard E, Niyyati M, Lorenzo-Morales J et al (2017) Molecular identification of waterborne free living amoebae (Acanthamoeba, Naegleria and Vermamoeba) isolated from municipal drinking water and environmental sources, Semnan province, north half of Iran. Exp Parasitol 183:240–244. https://doi.org/10.1016/j.exppara.2017.09.016
Ji WT, Hsu BM, Chang TY et al (2014) Surveillance and evaluation of the infection risk of free-living amoebae and Legionella in different aquatic environments. Sci Total Environ 499:212–219. https://doi.org/10.1016/j.scitotenv.2014.07.116
Johnson RO, Cope JR, Moskowitz M et al MJ (2016) Notes from the Field: primary amebic meningoencephalitis associated with exposure to swimming pool water supplied by an overland pipe - Inyo County, California, 2015. MMWR Morb Mortal Wkly Rep. 65(16):424. https://doi.org/10.15585/mmwr.mm6516a4
Kang H, Sohn HJ, Seo GE et al (2020) Molecular detection of free-living amoebae from Namhangang (southern Han River) in Korea. Sci Rep 10(1):335. https://doi.org/10.1038/s41598-019-57347-1
Kao PM, Hsu BM, Chen NH et al (2012) Isolation and identification of Acanthamoeba species from thermal spring environments in southern Taiwan. Exp Parasitol 130(4):354–358. https://doi.org/10.1016/j.exppara.2012.02.008
Kao P-M, Hsu B-M, Chiu Y-C et al (2012) Identification of the Naegleria species in natural watersheds used for drinking and recreational purposes in Taiwan. J Environ Eng 138(8):893–898. https://doi.org/10.1061/(ASCE)EE.1943-7870.0000549
Kao PM, Tung MC, Hsu BM et al (2012) Occurrence and distribution of Naegleria species from thermal spring environments in Taiwan. Lett Appl Microbiol 56(1):1–7. https://doi.org/10.1111/lam.12006
Kao PM, Tung MC, Hsu BM et al (2013a) Quantitative detection and identification of Naegleria spp. in various environmental water samples using real-time quantitative PCR assay. Parasitol Res 112(4):1467–74. https://doi.org/10.1007/s00436-013-3290-x
Kao PM, Tung MC, Hsu BM et al (2013) Real-time PCR method for the detection and quantification of Acanthamoeba species in various types of water samples. Parasitol Res 112(3):1131–1136. https://doi.org/10.1007/s00436-012-3242-x
Kiss C, Barna Z, Vargha M, Török JK (2014) Incidence and molecular diversity of Acanthamoeba species isolated from public baths in Hungary. Parasitol Res 113:2551–2557. https://doi.org/10.1007/s00436-014-3905-x
Król-Turmińska K, Olender A (2017) Human infections caused by free-living amoebae. Ann Agric Environ Med 24(2):254–260. https://doi.org/10.5604/12321966.1233568
Landell MF, Salton J, Caumo K (2013) Isolation and genotyping of free-living environmental isolates of Acanthamoeba spp. from bromeliads in Southern Brazil. Exp Parasitol 134(3):290–4. https://doi.org/10.1016/j.exppara.2013.03.028
Lares-Jiménez LF, Borquez-Román MA, Lares-García C et al (2018) Potentially pathogenic genera of free-living amoebae coexisting in a thermal spring. Exp Parasitol 195:54–58. https://doi.org/10.1016/j.exppara.2018.10.006
Lares-Villa F, Hernández-Peña C (2010) Concentration of Naegleria fowleri in natural waters used for recreational purposes in Sonora, Mexico (November 2007-October 2008). Exp Parasitol 126(1):33–36. https://doi.org/10.1016/j.exppara.2010.04.011
Latiff NSA, Jali A, Azmi NA et al (2018) A ocorrência de Acanthamoeba e Naegleria em águas recreativas de fontes termais selecionadas em Selangor, Malásia. Int J Trop Med 13(3):21–24
Latifi A, Salami M, Kazemirad E, Soleimani M (2020) Isolation and identification of free-living amoeba from the hot springs and beaches of the Caspian Sea. Parasite Epidemiol Control 10:e00151. https://doi.org/10.1016/j.parepi.2020.e00151
Latifi AR, Niyyati M, Lorenzo-Morales J et al (2016) Presence of Balamuthia mandrillaris in hot springs from Mazandaran province, northern Iran. Epidemiol Infect 144(11):2456–2461. https://doi.org/10.1017/S095026881600073X
Latifi AR, Niyyati M, Lorenzo-Morales J et al (2017) Occurrence of Naegleria species in therapeutic geothermal water sources. North Iran Acta Parasitol 62(1):104–109. https://doi.org/10.1515/ap-2017-0012
Lekkla A, Sutthikornchai C, Bovornkitti S, Sukthana Y (2005) Free-living ameba contamination in natural hot springs in Thailand. SE Asian J Trop Med Public Health 36(4):5–9
Lyons TB, Kapur R (1977) Limax amoebae in public swimming pools of Albany, Schenectady, and Rensselaer Counties, New York: their concentration, correlations, and significance. Appl Environ Microbiol 33(3):551–555. https://doi.org/10.1128/aem.33.3.551-555.1977
Mafi M, Niyyati M, Haghighi A, Lasjerdi Z (2017) Contamination of swimming pools and park ponds with free living amoebae in Tehran. Med J Tabriz Uni Med Sciences Health Services 38(6):2783–2031. https://mj.tbzmed.ac.ir/Article/15215
Maghsoodloorad S, Maghsoodloorad E, Tavakoli Kareshk A et al (2019) Thermotolerant Acanthamoeba spp. isolated from recreational water in Gorgan City, north of Iran. J Parasit Dis 43(2):240–245. https://doi.org/10.1007/s12639-018-01081-4
Mahmoudi MR, Rahmati B, Seyedpour SH, Karanis P (2015) Occurrence and molecular characterization of free-living amoeba species (Acanthamoeba, Hartmannella, and Saccamoeba limax) in various surface water resources of Iran. Parasitol Res 114(12):4669–4674. https://doi.org/10.1007/s00436-015-4712-8
Majid MAA, Mahboob T, Mong BG et al (2017) Pathogenic waterborne free-living amoebae: an update from selected Southeast Asian countries. PLoS ONE 12(2):e0169448. https://doi.org/10.1371/journal.pone.0169448
Maschio JV, Corção G, Rott MB (2015) Identification of Pseudomonas spp. as amoeba-resistant microorganisms in isolates of Acanthamoeba. Rev Inst Med Trop Sao Paulo 57(1):81–83. https://doi.org/10.1590/S0036-46652015000100012
Mavridou A, Pappa O, Papatzitze O et al (2018) Exotic tourist destinations and transmission of infections by swimming pools and hot springs-a literature review. Int J Environ Res Public Health 15(12):2730. https://doi.org/10.3390/ijerph15122730
Milanez GD, Masangkay FR, Martin IGL (2022) Epidemiology of free-living amoebae in the Philippines: a review and update. Pathog Glob Health 3:1–10. https://doi.org/10.1080/20477724.2022.2035626
Moussa M, De Jonckheere JF, Guerlotté J et al (2013) Survey of Naegleria fowleri in geothermal recreational waters of Guadeloupe (French West Indies). PLoS ONE 8(1):e54414. https://doi.org/10.1371/journal.pone.0054414
Munoz V, Reyes H, Toche P et al (2003) Isolation of free living amoebae from public swimming pool in Santiago, Chile. Parasitologia Latinoamericana 58(3/4):106–111. https://eurekamag.com/research/004/215/004215933.php
Murakawa GJ, McCalmont T, Altman J et al (1995) Disseminated acanthamebiasis in patients with AIDS. A report of five cases and a review of the literature. Arch Dermatol. 131(11):1291–1296. https://doi.org/10.1001/archderm.1995.01690230069011
Nageeb MM, Eldeek HEM, Attia RAH et al (2022) Isolation and morphological and molecular characterization of waterborne free-living amoebae: evidence of potentially pathogenic Acanthamoeba and Vahlkampfiidae in Assiut, Upper Egypt. Plos One 17(7):e0267591. https://doi.org/10.1371/journal.pone.0267591
Nazar M, Haghighi A, Niyyati M et al (2011) Genotyping of Acanthamoeba isolated from water in recreational areas of Tehran, Iran. J Water Health 9(3):603–608. https://doi.org/10.2166/wh.2011.152
Nazar M, Haghighi A, Taghipour N et al (2012) Molecular identification of Hartmannella vermiformis and Vannella persistens from man-made recreational water environments, Tehran, Iran. Parasitol Res 111:835–839. https://doi.org/10.1007/s00436-012-2906-x
Nisar MA, Ross KE, Brown MH et al (2020) Legionella pneumophila and protozoan hosts: implications for the control of hospital and potable water systems. Pathogens 9(4):286. https://doi.org/10.3390/pathogens9040286
Niyyati M, Lasjerdi Z, Nazar M et al (2012) Screening of recreational areas of rivers for potentially pathogenic free-living amoebae in the suburbs of Tehran. Iran J Water Health 10(1):140–146. https://doi.org/10.2166/wh.2011.068
Niyyati M, Lasjerdi Z, Zarein-Dolab S et al (2015a) Morphological and molecular survey of Naegleria spp. in water bodies used for recreational purposes in Rasht city, Northern Iran. Iran J Parasitol 10(4):523–529
Niyyati M, Nazar M, Lasjerdi Z (2015b) Reporting of T4 genotype of Acanthamoeba isolates in recreational water sources of Gilan Province, Northern Iran. Novel Biomed 3(1):20–4. https://doi.org/10.22037/nbm.v3i1.7177
Niyyati M, Saberi R, Latifi A, Lasjerdi Z (2016) Distribution of Acanthamoeba genotypes isolated from recreational and therapeutic geothermal water sources in Southwestern Iran. Environ Health Insights 10:69–74. https://doi.org/10.4137/EHI.S38349
Niyyati M, Saberi R, Lorenzo-Morales J, Salehi R (2016) High occurrence of potentially-pathogenic free-living amoebae in tap water and recreational water sources in South-West Iran. Trop Biomed 33(1):95–101
Onichandran S, Kumar T, Salibay CC (2014) Waterborne parasites: a current status from the Philippines. Parasit Vectors 7:244. https://doi.org/10.1186/1756-3305-7-244
Page MJ, McKenzie JE, Bossuyt PM et al (2021) The PRISMA 2020 statement: an updated guideline for reporting systematic reviews. BMJ (Clin Res Ed) 372:71. https://doi.org/10.1136/bmj.n71
Paknejad N, Hajialilo E, Saraei M, Javadi A (2020) Isolation and identification of Acanthamoeba genotypes and Naegleria spp. from the water samples of public swimming pools in Qazvin, Iran. J Water Health 18(2):244–251. https://doi.org/10.2166/wh.2019.074
Paltiel M, Powell E, Lynch J et al (2004) Disseminated cutaneous acanthamebiasis: a case report and review of the literature. Cutis 73(4):241–248
Pazoki H, Niyyati M, Javanmard E et al (2020) Isolation and phylogenetic analysis of free-living amoebae (Acanthamoeba, Naegleria, and Vermamoeba) in the farmland soils and recreational places in Iran. Acta Parasitol 65(1):36–43. https://doi.org/10.2478/s11686-019-00126-9
Penas-Ares M, Paniagua-Crespo E, Madriñan-Choren R et al (1994) Isolation of free-living pathogenic amoebae from thermal spas in N.W Spain. Water Air Soil Pollut 78:83–90. https://doi.org/10.1007/BF00475670
Pernin P, Riany A (1978) Etude sur la présence d’amibes libres’ dans les eaux des piscines lyonnaises [Study on the presence of “free-living” amoebae in the swimming-pools of Lyon (author’s transl)]. Ann Parasitol Hum Comp 53(4):333–44. French
Poor BM, Dalimi A, Ghafarifar F et al (2018) Contamination of swimming pools and hot tubs biofilms with Acanthamoeba. Acta Parasit 63:147–153. https://doi.org/10.1515/ap-2018-0016
Rahdar M, Niyyati M, Salehi M et al (2012) Isolation and genotyping of Acanthamoeba strains from environmental sources in Ahvaz City, Khuzestan Province, Southern Iran. Iran J Parasitol 7(4):22–26
Rayamajhee B, Subedi D, Peguda HK (2021) A systematic review of intracellular microorganisms within Acanthamoeba to understand potential impact for infection. Pathogens (Basel, Switzerland) 10(2):225. https://doi.org/10.3390/pathogens10020225
Reyes-Batlle M, Gabriel MF, Rodríguez-Expósito R et al (2021) Evaluation of the occurrence of pathogenic free-living amoeba and bacteria in 20 public indoor swimming pool facilities. MicrobiologyOpen 10(1):e1159. https://doi.org/10.1002/mbo3.1159
Reyes-Batlle M, Wagner C, López-Arencibia A et al (2017) Isolation and molecular characterization of a Naegleria strain from a recreational water fountain in Tenerife, Canary Islands. Spain Acta Parasitol 62(2):265–268. https://doi.org/10.1515/ap-2017-0033
Rezaeian M, Niyyati M, Farnia Sh, Haghi AM (2008) Isolation of Acanthamoeba spp. from different environmental sources. Iranian J Parasitol 3(1):44–47
Rivera F, Ramírez E, Bonilla P et al (1993) Pathogenic and free-living amoebae isolated from swimming pools and physiotherapy tubs in Mexico. Environ Res 62(1):43–52. https://doi.org/10.1006/enrs.1993.1087
Rivera F, Ramírez P, Vilaclara G et al (1983) A survey of pathogenic and free-living amoebae inhabiting swimming pool water in Mexico City. Environ Res 32(1):205–211. https://doi.org/10.1016/0013-9351(83)90207-4
Rocha MJ, Sousa KK, Carneiro JLS, Weber DM, (2022 Isolation of potentially pathogenic free-living amoebae in swimming pools for collective use located in the municipality of Redenção, Pará, Brazil. Rev Ciênc Med 31:e225222. https://doi.org/10.24220/2318- 0897v31e2022a5222
Saberi R, Seifi Z, Dodangeh S et al et al (2020) A systematic literature review and meta-analysis on the global prevalence of Naegleria spp. in water sources. Transbound Emerg Dis. 67(6):2389–2402. https://doi.org/10.1111/tbed.13635
Saberi R, Fakhar M, Makhlough A, Sedighi O, Tabaripour R, Asfaram S, Latifi A, Espahbodi F, Sharifpour A (2021) First evidence for colonizing of acanthamoeba T4 genotype in urinary tracts of patients with recurrent urinary tract infections. Acta Parasitologica 66(3):932–937. https://doi.org/10.1007/s11686-021-00358-8
Saburi E, Rajaii T, Behdari A et al (2017) Free-living amoebae in the water resources of Iran: a systematic review. J Parasit Dis 41(4):919–928. https://doi.org/10.1007/s12639-017-0950-2
Salehi M, Niazkar HR, Nasirzadeh A (2019) Isolation and genotyping of Acanthamoeba strains from water sources of Kermanshah, Iran. Ann Parasitol 65(4):397–402. https://doi.org/10.17420/ap6504.226
Salehi M, Spotin A, Hajizadeh F et al (2022) Molecular characterization of Acanthamoeba spp. from different sources in Gonabad, Razavi Khorasan, Iran. Gene Reports 27:101573. https://doi.org/10.1016/j.genrep.2022.101573
Santos DL, Virginio VG, Kwitko S et al (2021) Profile of contact lens wearers and associated risk factors for Acanthamoeba spp., In: Nascimento RM (ed) Microbiologia: clínica, ambiental e alimentos. Editora Atena, cap. 14:151–161. https://doi.org/10.22533/at.ed.543210120
Santos LC, Oliveira MS, Lobo RD et al (2009) Acanthamoeba spp. in urine of critically ill patients. Emerg Infect Dis 15(7):1144–1146. https://doi.org/10.3201/eid1507.081415
Sarink MJ, van der Meijs NL, Denzer K et al (2022) Three encephalitis-causing amoebae and their distinct interactions with the host. Trends Parasitol 38(3):230–245. https://doi.org/10.1016/j.pt.2021.10.004
Sarmadian H, Hazbavi Y, Didehdar M et al (2020) Fungal and parasitic contamination of indoor public swimming pools in Arak, Iran. J Egypt Public Health Assoc 95(1):8. https://doi.org/10.1186/s42506-020-0036-3
Scaglia M, Gatti S, Brustia R et al (1987) Pathogenic and non-pathogenic Naegleria and Acanthamoeba spp.: a new autochthonous isolate from an Italyn thermal area. Microbiologica 10(2):171–82
Scaglia M, Strosselli M, Grazioli V et al (1983) Isolation and identification of pathogenic Naegleria australiensis (Amoebida, Vahlkampfiidae) from a spa in northern Italy. Appl Environ Microbiol 46(6):1282–1285. https://doi.org/10.1128/aem.46.6.1282-1285.1983
Scheid P (2014) Relevance of free-living amoebae as hosts for phylogenetically diverse microorganisms. Parasitol Res 113(7):2407–2414. https://doi.org/10.1007/s00436-014-3932-7
Sheehan KB, Fagg JA, Ferris MJ et al (2003) PCR detection and analysis of the free-living amoeba Naegleria in hot springs in Yellowstone and Grand Teton National Parks. Appl Environ Microbiol 69(10):5914–5918. https://doi.org/10.1128/AEM.69.10.5914-5918.2003
Siddiqui R, Khan NA (2014) Primary amoebic meningoencephalitis caused by Naegleria fowleri: an old enemy presenting new challenges. PLoS Negl Trop Dis 8:e3017. https://doi.org/10.1371/journal.pntd.0003017
Sifuentes LY, Choate BL, Gerba CP et al (2014) The occurrence of Naegleria fowleri in recreational waters in Arizona. J Environ Sci Health A Tox Hazard Subst Environ Eng 49(11):1322–1330. https://doi.org/10.1080/10934529.2014.910342
Soares SS, Souza TK, Berté FK et al (2017) Occurrence of infected free-living amoebae in cooling towers of Southern Brazil. Curr Microbiol 74(12):1461–1468. https://doi.org/10.1007/s00284-017-1341-8
Solgi R, Niyyati M, Haghighi A et al (2012a) Thermotolerant Acanthamoeba spp. isolated from therapeutic hot springs in Northwestern Iran. J Water Health 10(4):650–6. https://doi.org/10.2166/wh.2012.032
Solgi R, Niyyati M, Haghighi A, Mojarad EN (2012b) Occurrence of thermotolerant Hartmannella vermiformis and Naegleria spp. in hot springs of Ardebil Province, Northwest Iran. Iran J Parasitol 7(2):47–52
Sousa-Ramos D, Reyes-Batlle M, Bellini NK et al (2022) Pathogenic free-living amoebae from water sources in Cape Verde. Parasitol Res 121(8):2399–2404. https://doi.org/10.1007/s00436-022-07563-y
Staggemeier R, Arantes T, Caumo KS et al (2016) Detection and quantification of human adenovirus genomes in Acanthamoeba isolated from swimming pools. An Acad Bras Cienc 88(1):635–641. https://doi.org/10.1590/0001-3765201620150151
Stapleton F (2021) The epidemiology of infectious keratitis. Ocul Surf S1542–0124(21):00089–00096. https://doi.org/10.1016/j.jtos.2021.08.007
Sukthana Y, Lekkla A, Sutthikornchai C et al (2005) Spa, springs and safety. SE Asian J Trop Med Public Health 36(Suppl 4):10–16
Thomas V, Bouchez T, Nicolas V et al (2004) Amoebae in domestic water systems: resistance to disinfection treatments and implication in Legionella persistence. J Appl Microbiol 97:950–963. https://doi.org/10.1111/j.1365-2672.2004.02391.x
Thomas V, Loret JF, Jousset M, Greub G (2008) Biodiversity of amoebae and amoebae-resisting bacteria in a drinking water treatment plant. Environ Microbiol 102728–2745.https://doi.org/10.1111/j.1462-2920.2008.01693.x
Todd CD, Reyes-Batlle M, Piñero JE et al (2015) Isolation and molecular characterization of Acanthamoeba genotypes in recreational and domestic water sources from Jamaica, West Indies. J Water Health 13(3):909–919. https://doi.org/10.2166/wh.2015.232
Toula FH, Elahl SAS (2017) Isolation and identification of free living amoebae from water sources with respect to Acanthamoeba, Naegleria in Jeddah City, Saudi Arabia. Int J Pharm Res Allied Sci 6(2):01–08
Tsvetkova N, Schild M, Panaiotov S et al (2004) The identification of free-living environmental isolates of amoebae from Bulgaria. Parasitol Res 92(5):405–413. https://doi.org/10.1007/s00436-003-1052-x
Tung MC, Hsu BM, Tao CW et al (2013) Identification and significance of Naegleria fowleri isolated from the hot spring which related to the first primary amebic meningoencephalitis (PAM) patient in Taiwan. Int J Parasitol 43(9):691–696. https://doi.org/10.1016/j.ijpara.2013.01.012
Turankar RP, Lavania M, Darlong J, Siva Sai KSR, Sengupta U, Jadhav RS (2019) Survival of Mycobacterium leprae and association with Acanthamoeba from environmental samples in the inhabitant areas of active leprosy cases: a cross sectional study from endemic pockets of Purulia, West Bengal. Infect Genet Evol 72:199–204. https://doi.org/10.1016/j.meegid.2019.01.014
Vesaluoma M, Kalso S, Jokipii L et al (1995) Microbiological quality in Finnish public swimming pools and whirlpools with special reference to free living amoebae: a risk factor for contact lens wearers? Br J Ophthalmol 79(2):178–181. https://doi.org/10.1136/bjo.79.2.178
Vijayakumar R (2018) Isolation, identification of pathogenic Acanthamoeba from drinking and recreational water sources in Saudi Arabia. J Adv Vet Anim Res 5(4):439–444. https://doi.org/10.5455/javar.2018.e296
Visvesvara GS, Moura H, Schuster FL (2007) Pathogenic and opportunistic free-living amoebae: Acanthamoeba spp., Balamuthia mandrillaris, Naegleria fowleri, and Sappinia diploidea. FEMS Immunol Med Microbiol 50(1):1–26. https://doi.org/10.1111/j.1574-695X.2007.00232.x
Wopereis DB, Bazzo ML, de Macedo JP et al (2020) Free-living amoebae and their relationship to air quality in hospital environments: characterization of Acanthamoeba spp. obtained from air-conditioning systems. Parasitology. 147(7):782–790. https://doi.org/10.1017/S0031182020000487
Xue J, Lamar FG, Zhang B (2018) Quantitative assessment of Naegleria fowleri and fecal indicator bacteria in brackish water of Lake Pontchartrain. Louisiana Sci Total Environ 622–623:8–16. https://doi.org/10.1016/j.scitotenv.2017.11.308
Zeybek Z, Demir B, Ustunturk-Onan M (2017) Unnoticed microorganisms in disinfection of swimming pools: free-living amoeba. Fresenius Environ Bull 26(12A):7651–7657
Zeybek Z, Türkmen A (2020) Investigation of the incidence of Legionella and free-living amoebae in swimming pool waters and biofilm specimeNs in Istanbul by different methods. Mikrobiyol Bul 54(1):50–65. https://doi.org/10.5578/mb.68962
Zhou P, Giovanni GDD, Meschke JS et al (2014) Enhanced inactivation of Cryptosporidium parvum oocysts during solar photolysis of free available chlorine. Environ Sci Technol Lett 1(11):453–458. https://doi.org/10.1021/ez500270u
Acknowledgements
The authors would like to thank CAPES (Coordenação de Aperfeiçoamento de Pessoal de Nível Superior) for the scholarship granted to Chaúque, BJM, and CNPq for the researcher grant to Rott, MB.
Author information
Authors and Affiliations
Contributions
B.J.M.C. conceived the idea, wrote the project, collected and analyzed the data, and wrote the manuscript. D.S. participated in the conception of the idea, performed the data verification, and wrote and revised the manuscript. D.A. performed data analysis and manuscript review. M.B.R. managed the project and reviewed the manuscript. All authors approved the publication of this version of the manuscript.
Corresponding author
Ethics declarations
Ethics approval
Not applicable.
Consent to participate
Not applicable.
Consent for publication
Not applicable.
Conflict of interest
The authors declare no competing interests.
Additional information
Handling Editor: Sutherland Maciver
Publisher's note
Springer Nature remains neutral with regard to jurisdictional claims in published maps and institutional affiliations.
Supplementary information
Below is the link to the electronic supplementary material.
Rights and permissions
Springer Nature or its licensor holds exclusive rights to this article under a publishing agreement with the author(s) or other rightsholder(s); author self-archiving of the accepted manuscript version of this article is solely governed by the terms of such publishing agreement and applicable law.
About this article
Cite this article
Chaúque, B.J.M., dos Santos, D.L., Anvari, D. et al. Prevalence of free-living amoebae in swimming pools and recreational waters, a systematic review and meta-analysis. Parasitol Res 121, 3033–3050 (2022). https://doi.org/10.1007/s00436-022-07631-3
Received:
Accepted:
Published:
Issue Date:
DOI: https://doi.org/10.1007/s00436-022-07631-3