Persistence of Pseudomonas aeruginosa in chlorinated swimming pools

1980 ◽  
Vol 26 (3) ◽  
pp. 350-355 ◽  
Author(s):  
Patricia L. Seyfried ◽  
David J. Fraser

Various types of swimming pools were investigated for the quantitative isolation of Pseudomonas aeruginosa. Incidence of the organism increased when the free chlorine residual dropped below 0.4 mg/L in pool water which had a pH of 6.9–7.8. As the water pH became more alkaline the efficiency of disinfection decreased. Excessive slime production caused certain strains to become more resistant to chlorine treatment. Immunotyping and phage typing, used to study the dynamics of P. aeruginosa populations in swimming pool waters, demonstrated that high densities of the organism consisted mainly of single predominant strains.

2008 ◽  
Vol 7 (1) ◽  
pp. 109-114 ◽  
Author(s):  
Joan M. Shields ◽  
Michael J. Arrowood ◽  
Vincent R. Hill ◽  
Michael J. Beach

Cyanuric acid is used to stabilize free chlorine to reduce photodegradation in outdoor swimming pools. While there have been numerous studies examining its effect on the disinfection rates of bacteria and viruses, it is not known whether cyanuric acid can significantly impact the effectiveness of hyperchlorination for inactivating Cryptosporidium oocysts present in fecally-contaminated swimming pools. This study examined the effect of cyanuric acid on the disinfection rate of Cryptosporidium parvum under swimming pool hyperchlorination conditions (20 mg/ml free chlorine). When 50 mg/L cyanuric acid was present there was a 0.70-log10 reduction in oocyst viability after 10 hours as compared to a 3.7-log10 reduction without cyanuric acid. Aids to remediation, such as decreasing the pH to enhance the germicidal efficiency of the free chlorine and doubling the amount of free chlorine residual, were still unable to achieve a 3-log10 reduction. Current public health recommendations for hyperchlorination and pool remediation are insufficient for pools using cyanurate-stabilized chlorine to achieve a three log inactivation of the parasite.


1974 ◽  
Vol 73 (2) ◽  
pp. 213-220 ◽  
Author(s):  
P. B. Crone ◽  
G. H. Tee

SUMMARYDuring a period of five years 1192 water samples from swimming pools were examined for staphylococci and 338 for coliform organisms only. Eighty-nine different pools were sampled.Numbers of staphylococci, estimated by the membrane filtration technique did not bear any significant relation to either bathing load or concentration of free chlorine.Wide variation in the staphylococcal count was observed when different parts of a pool were sampled on the same occasion.The only practicable standard for pool samples in relation to staphylococci would appear to be that these organisms should be absent from 100 ml. water when the pool has been out of use during at least ten hours before sampling if filtration and chlorination are adequate.


Author(s):  
Marco Guida ◽  
Valeria Di Onofrio ◽  
Francesca Gallè ◽  
Renato Gesuele ◽  
Federica Valeriani ◽  
...  

1991 ◽  
Vol 107 (3) ◽  
pp. 497-508 ◽  
Author(s):  
R. E. Joce ◽  
J. Bruce ◽  
D. Kiely ◽  
N. D. Noah ◽  
W. B. Dempster ◽  
...  

SUMMARYIn August 1988 an increase was noted in the number of cases of cryptosporidiosis identified by the microbiology laboratory at Doncaster Royal Infirmary. By 31 October, 67 cases had been reported. Preliminary investigations implicated the use of one of two swimming pools at a local sports centre and oocysts were identified in the pool water. Inspection of the pool revealed significant plumbing defects which had allowed ingress of sewage from the main sewer into the circulating pool water. Epidemiological investigation confirmed an association between head immersion and illness. The pools were closed when oocysts were identified in the water and extensive cleaning and repair work was undertaken. The pool water was retested for cryptosporidial oocysts and found to be negative before the pool re-opened.


2021 ◽  
pp. 124-128
Author(s):  
К. V. Solomakha

The coronavirus pandemic has changed the usual way of life of almost every one of us, all areas have shifted to work with limited functioning and activities in quarantine. SARS-CoV-2, the causative agent of COVID-19, is mostly transmitted from person to person by close contact through small droplets (released during coughing, sneezing and talking) contaminated with the virus, or virus particles that linger in the air for several minutes to several hours, less often infection occurs through contaminated surfaces and objects. The objective was to analyze the possibility of safe operation of water complexes (water parks, swimming pools, etc.) during a pandemic COVID-19 in our country. Materials and methods. Since November 2019 and so far, we have been taking water samples from one private pool and from the pool of a sports complex in one University in Kyiv, in addition, because of cooperation with the Brovary Regional Department of Laboratory Research of the State Institution «Kyiv Regional Laboratory Center of the Ministry of Health of Ukraine» we have known the results of water control in one under roof water park in Brovary, which is located in Kyiv region. We explored the quality of water by sanitary chemical indices (odor, color, turbidity, pH, water hardness, concentration of ammonia and ammonium ions, chlorides, sulfates, free chlorine, etc.) and microbiological indicators (total microbial count (TMC) and coli bacterial index (index of bacteria of the group of E. coli (CBI)). Results of the research. In our research, we analyzed the guidelines on the possibility and conditions of the functioning of water complexes during quarantine restrictions of various countries. We found that the free chlorine level in water samples complies to those recommendation, which WHO is provided in the context of the coronavirus pandemic in private and public water complexes. Currently, there are no studies that suggest the possibility of survival of SARS-CoV-2 virus in swimming pool water or other water entertainment complexes, although experimental data obtained previously with coronaviruses (on cell cultures) other than SARS CoV-2, indicate that they are usually sensitive to strong oxidants, such as chlorine. Therefore, today, we can assume that purified water in swimming pools and other water complexes is not an environment where the SARS-CoV-2 virus can survive. The WHO states that a residual free chlorine concentration ≥ 0.5 mg / L in pool water at pH < 8,0 is sufficient to kill coronaviruses. The virus that causes COVID-19 has been found in the fecal matter of infected people, not just those with symptoms of gastrointestinal disorders. It's generally believed that the excretion of the virus may persist for several days. However, it should be noted that there are no cases of fecal-oral transmission of SARS-CoV-2 now. Therefore, to date, the risk of SARS-CoV-2 transmission by fecal-oral route is assessed as low. Conclusions. According to the data from lead countries regarding recommendations for visiting water complexes during the COVID-19 pandemic and because of the lack of our own research in our country, we can talk about the possibility of their implementation in Ukraine. We believe that the constant closure of swimming pools and water complexes, and, consequently, constant breaks in the training of not only professional athletes, but also amateurs, run counter to the recommendations regarding the promotion of a healthy lifestyle. It`s worth to remember that prevention is always better than treatment, and training sports is one of the key points in ensuring the effective work of the body and the immune system in particular, which is especially important during a pandemic.


2018 ◽  
Vol 16 (6) ◽  
pp. 861-892 ◽  
Author(s):  
Huma Ilyas ◽  
Ilyas Masih ◽  
Jan Peter van der Hoek

Abstract This paper investigates disinfection by-products (DBPs) formation and their relationship with governing factors in chlorinated swimming pools. The study compares concentrations of DBPs with WHO guidelines for drinking water quality recommended to screen swimming pool water quality. The statistical analysis is based on a global database of 188 swimming pools accumulated from 42 peer-reviewed journal publications from 16 countries. The mean and standard deviation of dichloroacetic acid and trichloroacetic acid were estimated as 282 ± 437 and 326 ± 517 μg L−1, respectively, which most often surpassed the WHO guidelines. Similarly, more than half of the examined pools had higher values of chloral hydrate (102 ± 128 μg L−1). The concentration of total chloramines (650 ± 490 μg L−1) was well above the WHO guidelines in all reported cases. Nevertheless, the reported values remained below the guidelines for most of the studied pools in the case of total trihalomethanes (134 ± 160 μg L−1), dichloroacetonitrile (12 ± 12 μg L−1) and dibromoacetonitrile (8 ± 11 μg L−1). Total organic carbon, free residual chlorine, temperature, pH, total nitrogen and bromide ions play a pivotal role in DBPs formation processes. Therefore, proper management of these governing factors could significantly reduce DBPs formation, thereby, contributing towards a healthy swimming pool environment.


2005 ◽  
Vol 52 (8) ◽  
pp. 71-76 ◽  
Author(s):  
W. Uhl ◽  
C. Hartmann

For swimming pools, it is generally agreed that free chlorine levels have to be maintained to guarantee adequate disinfection. Recommended free chlorine levels can vary between 0.3 and 0.6mg/L in Germany and up to 3mg/L in other countries. Bathers introduce considerable amounts of organic matter, mainly in the form of such as urine and sweat, into the pool water. As a consequence, disinfection byproducts (DBPs) are formed. Regulations in Germany recommend levels of combined chlorine of less than 0.2mg/L and levels of trihalomethanes (THMs) of less than 20μg/L. Haloacetic acids (HAAs), haloacetonitriles (HANs), chloropicrin and chloral hydrate are also detected in considerable amounts. However, these compounds are not regulated yet. Swimming pool staff and swimmers, especially athletes, are primarily exposed to these byproducts by inhalation and/or dermal uptake. In Germany, new regulations for swimming pool water treatment generally require the use of activated carbon. In this project, three different types of granular activated carbon (GAC) (one standard GAC, two catalytic GACs) are compared for their long time behaviour in pool water treatment. In a pilot plant operated with real swimming pool water, production and removal of disinfection byproducts (THMs, HAAs, AOXs), of biodegradable substances (AOC), of bacteria (Pseudomonas aeruginosa, Legionella, coliforms, HPC) as well as the removal of chlorine and chloramines are monitored as function of GAC bed depth. Combined chlorine penetrates deeper in the filter bed than free chlorine does. However, both, free and combined chlorine removal efficiencies decrease over the time of filter operation. The decreases of removal efficiencies are also observed for parameters such as dissolved organic carbon, spectral absorption coefficient, adsorbable organic carbon and most of the disinfection byproducts. However, THMs, especially chloroform are produced in the filter bed. The GAC beds were contaminated microbially, especially with P. aeruginosa. The contamination was not removable by backwashing with chlorine concentrations up to 2mg/l free chlorine.


2021 ◽  
Vol 9 (1) ◽  
pp. 38
Author(s):  
Anna Lempart-Rapacewicz ◽  
Edyta Kudlek ◽  
Mariusz Dudziak ◽  
Marta Dyrała

The study assessed unfavorable phenomena occurring in swimming pool water, including the occurrence of organic micropollutants in swimming pools and the transformation of these compounds during the swimming pool water treatment processes. The presence of three selected compounds was examined from the personal care products group (PCP) in pool water samples, collected in 2018 and 2019, from fifteen pools characterized using three different solutions of swimming pool water treatment systems. In addition, experimental studies on the effects of UV radiation and ozone on selected organic micropollutants, previously identified in swimming pools and the relationship between swimming pool water turbidity and the concentration of the selected PCP micropollutants, were carried out


1989 ◽  
Vol 21 (2) ◽  
pp. 151-160 ◽  
Author(s):  
D. E. J. Powick

A brief history of the development of swimming pool water treatment and management has been discussed, applicable to both large and small pools. An outline of typical bathing loads and current methods of water treatment has been presented with particular emphasis being given to disinfection. Chlorine has been the traditional sole disinfectant used since the 1920's but alternatives are continually being sought. Chief amongst the alternatives to date has been ozone, used in conjunction with chlorine. Ozone acts as a powerful oxidiser and disinfectant but has little residual effect. Chlorine is therefore used to provide a residual in the pool. Current British trends in pool design and treatment have been noted.


1981 ◽  
Vol 86 (3) ◽  
pp. 357-362 ◽  
Author(s):  
T. M. S. Reid ◽  
I. A. Porter

SUMMARYPseudomonas aeruginosawas isolated from the ears of 18 of the 25 members of a team of competitive swimmers who complained of painful discharging ears. This group of swimmers trained twice daily in the pool, in the early morning and late afternoon. In contrast swabbing of the ears of a similar group of 54 competitive swimmers who used the pool only in the afternoon revealed only one swimmer withP. aeruginosa.Investigation of the swimming pool revealed that chlorination was often inadequate when the first group of swimmers were training in the early morning. Strains ofP. aeruginosawere isolated from various sites around the pool and from the bag of a vacuum used to clean the pool.Pyocin typing, serotyping and phage typing were performed on all isolates. The dominant strain recovered from the swimmers' ears was found to be almost identical to that from the vacuum bag and belonged to serotype 0–11 which has been particularly associated with outbreaks ofP. aeruginosainfection in whirlpools in the United States.These results support the hypothesis that there is a direct correlation between the development of otitis externa and swimming in water contaminated withP. aeruginosa.


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