January 2004
Volume 45, Issue 1
Immunology and Microbiology  |   January 2004
Acanthamoeba Keratitis: The Role of Domestic Tap Water Contamination in the United Kingdom
Author Affiliations
  • Simon Kilvington
    From the Department of Microbiology and Immunology, University of Leicester, Leicester, United Kingdom; the
  • Trevor Gray
    Department of Ophthalmology, Moorfields Eye Hospital, London, United Kingdom; the
  • John Dart
    Department of Ophthalmology, Moorfields Eye Hospital, London, United Kingdom; the
  • Nigel Morlet
    Department of Ophthalmology, Moorfields Eye Hospital, London, United Kingdom; the
  • John R. Beeching
    Department of Biology and Biochemistry, University of Bath, Bath, United Kingdom; the
  • David G. Frazer
    Department of Ophthalmology, Royal Victoria Hospital, Belfast, Northern Ireland; and the
  • Melville Matheson
    Department of Pathology, Institute of Ophthalmology, University of London, London, United Kingdom.
Investigative Ophthalmology & Visual Science January 2004, Vol.45, 165-169. doi:10.1167/iovs.03-0559
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      Simon Kilvington, Trevor Gray, John Dart, Nigel Morlet, John R. Beeching, David G. Frazer, Melville Matheson; Acanthamoeba Keratitis: The Role of Domestic Tap Water Contamination in the United Kingdom. Invest. Ophthalmol. Vis. Sci. 2004;45(1):165-169. doi: 10.1167/iovs.03-0559.

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      © 2015 Association for Research in Vision and Ophthalmology.

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purpose. The incidence of acanthamoeba keratitis (AK) in the UK is some 15 times that in the United States and seven times that in Holland. To investigate reasons for this higher frequency, a study of the role of domestic tap water as a potential source of AK was undertaken.

methods. Tap outlets from the homes of 27 patients with culture-proven AK were sampled and cultured for free-living amoebae (FLA). For all Acanthamoeba isolates, mitochondrial DNA (mtDNA) restriction fragment length polymorphisms (RFLPs) and cytochrome oxidase (cox 1/2) sequence typing was performed to determine the similarity between corneal and tap water isolates.

results. FLA, including Acanthamoeba, were isolated from 24 (89%) of 27 homes, and the presence within the homes varied significantly with tap water temperature and location: 19 (76%) of 25 bathroom sink cold taps sampled compared with 6 (24%) of 25 hot and 9 (47%) of 19 kitchen cold taps compared with 3 (16%) of 19 of hot kitchen taps. Acanthamoeba were isolated from 8 (30%) of 27 homes (five bathroom sink cold taps, one cloakroom cold tap, one bath, and one bedroom sink mixer [hot/cold] taps). In six cases, identical Acanthamoeba mtDNA profiles were found for the clinical and home tap water isolates. In keeping with UK plumbing practice, 24 of 27 homes had internal roof water storage tanks to supply domestic taps, but the mains fed the kitchen cold tap.

conclusions. Water storage tanks promote colonization of domestic water with FLA, including Acanthamoeba, and hence increase the risk of AK. This accounts for the significantly greater incidence of AK in the UK and supports advice to avoid using tap water in contact lens care routines.

The Acanthamoeba is a genus of free-living amoebae, members of which can cause a potentially blinding keratitis in humans. 1 The organism is characterized by a life cycle of feeding and replicating trophozoite and dormant cyst stages. 2 The resistance of Acanthamoeba cysts to most antimicrobial agents makes acanthamoeba keratitis one of the most difficult ocular infections to treat with a mean treatment period of more than 5 months, surgical interventions in 50% of cases, loss of vision (6/18 or less) in more than 30% of patients and, ultimately, enucleation in recalcitrant cases. 3 4 Contact lens wearers are most at risk of contracting acanthamoeba keratitis, accounting for some 90% of reported cases. 4 5 Poor hygiene practices, such as the failure to comply with recommended lens cleaning and disinfection procedures and the rinsing and storing of lenses in nonsterile saline or tap water are recognized risk factors for infection. 6 7 8 9  
Acanthamoeba is one of the most common free-living amoebae found in the environment. 2 Acanthamoeba cysts can withstand extremes of temperature, desiccation, and disinfection, 10 which accounts for the reported isolation of the organism from soil, mud, rivers, ponds, lakes, chlorinated bathing pools, water cooling towers, tap water, and the atmosphere. 8 11 12 This almost ubiquitous presence of Acanthamoeba in such environments is a constant challenge to the contact lens wearer as potential sources of infection. This also presents a difficulty in determining the precise source of a patient’s infection and is further complicated by the morphologic similarity between acanthamoeba keratitis strains. 10 13 However, the admission of many patients to rinsing or storing lenses in tap water or tap-water–prepared saline solutions has strongly implicated such practices to be a significant risk factor in acquiring the infection. 4 6 14  
Since acanthamoeba keratitis was recognized in 1973, several hundred cases have occurred in the UK, with 180 culture-positive cases treated at Moorfields Eye Hospital between January 1990 and December 2000; details of 183 cases are now in the literature. 3 5 15 Acanthamoeba keratitis is not a notifiable disease and therefore the true incidence of infection in the UK or worldwide is difficult to ascertain. However, studies have estimated the incidence among contact lens wearers to be 1.36 per million in the United States 14 (although studies using non–culture-based diagnostic methods have proposed an incidence one order of magnitude higher), 16 3.06 per million in Holland 17 and between 17.53 and 21.14 per million in the United Kingdom 4 9 15 ; however, it has been suggested that the incidence in England and Wales may be 33% higher than reported. 18  
In an attempt to explain the significantly higher incidence of acanthamoeba keratitis in the United Kingdom, we investigated the prevalence of Acanthamoeba in domestic water sources of 27 patients with culture-proven acanthamoeba keratitis. Mitochondrial DNA (mtDNA) typing was then used to compare Acanthamoeba corneal and domestic tap water isolates and provide a definite epidemiologic link for the source of infection. 
Twenty-seven patients with culture-proven acanthamoeba keratitis were investigated, of whom 23 were contact lens (CL) wearers. The study was retrospective, with a 3- to 10-month interval between corneal culture and obtaining domestic tap water samples. In addition, a previously unreported case from Northern Ireland was included. The study complied with the provisions of the Declaration of Helsinki. 
Domestic Water Sampling
Each patient was sent a sampling pack comprising a questionnaire and sterile cotton-tipped swabs individually contained in sterile plastic transport tubes (Bibby Sterilin, Staffordshire, UK). Written instructions indicated that before first daily use, each household tap should be sampled by rubbing the swab inside the spout of the tap and a little water from the tap run into the transport tube. The swab was then replaced into the tube sealed with adhesive tape and labeled according to tap location (e.g., bathroom sink, kitchen, bath) and temperature (hot, cold, or mixed hot/cold). The samples and completed questionnaire were then returned for analysis. 
Patients answered questions relating to possible risk factors for the development of acanthamoeba keratitis. These included CL wear, CL type, disinfection and storage methods, presence of a roof water storage cistern, CL contact with tap water, and CL wearing while swimming or when showering. 
In the laboratory, the tap samples were vortexed, and 0.5 mL of water inoculated over the surface of a nonnutrient agar plate seeded with a dense suspension of Escherichia coli (NNA-E. coli). 6 19 After the water had absorbed the plates were incubated at 32°C in sealed polythene bags and examined daily for up to 7 days using an inverted light microscope for the presence of FLA. Isolates of FLA were identified by morphologic examination of the trophozoite and cyst forms. 2 Acanthamoeba isolates were cloned by microcapillary manipulation of a single cyst on to a fresh NNA-E. coli plate. Excysted trophozoites from these clones were adapted to axenic (bacteria free) culture at 32°C. 13  
Mitochondrial DNA RFLP and Sequence Typing
Acanthamoeba isolates from the patients and domestic taps were compared for their mtDNA restriction fragment length polymorphisms (RFLPs). The mtDNA was isolated from axenic trophozoites by the alkaline lysis method used for the isolation of bacterial plasmid DNA, as previously applied to Acanthamoeba. 20 Approximately 2 to 3 μg of mtDNA was digested with the restriction endonuclease HindIII (Roche Diagnostics, Sussex, UK) and separated by electrophoresis in a 0.75% agarose gel at 2 V/cm for 18 hours in 0.5× TBE buffer. 21 DNA standards of λ-HindIII/ΦX-174 RF-HaeIII digests (Amersham Pharmacia Biotech, Milton Keynes, UK) were included as size markers. The gels were stained with 1.0 μg/mL ethidium bromide in distilled water and photographed under UV transillumination (665 film; Polaroid, Cambridge, MA; and a Wratten no. 9 orange filter; Eastman Kodak, Rochester, NY). 21  
PCR was used to amplify part of the cytochrome oxidase subunit-1 and -2 (cox1/2) from purified mtDNA (Cox-PCR). 22 Primers used were forward (gaattagctgctccgggttc) and reverse (tcaggataatcggggatccttc) designed to amplify a 1.2-kbp fragment. PCR was performed in a 50-μL volume consisting of: 1× Taq DNA polymerase buffer (20 mM (NH4)2SO4, 75 mM Tris-HCl [pH 8.8] at 25°C, 0.01% vol/vol Tween 20), 1.5 mM MgCl2, and 0.2 mM each dNTP, 0.5 μM of each primer, 1 U of Taq DNA polymerase (Red Hot; Advanced Biotechnologies Ltd., Epsom, UK) and approximately 100 ng of template DNA. Thermal cycling conditions were: 4 minutes 96°C, followed by 35 cycles of 1 minute 95°C, 1 minute 52°C, and 1.5 minutes 72°C. After a final 10 minutes at 72°C, samples were held at 4°C. Amplified products were analyzed by agarose gel electrophoresis and sent for sequencing (MWG-Biotech, AG, Ebersberg, Germany). DNA sequences were aligned (ClustalW) and a phylogenetic tree constructed (TreeView Win32 1.6.6; Uniersity of Glasgow, UK). 23 24  
Free-Living Amoebae
FLA were cultured from one or more taps of 24 (89%) of 27 households of acanthamoeba keratitis patients. FLA presence varied significantly with the tap water temperature and location. Water-main–supplied kitchen cold taps yielded 9 (47%) of 19 FLA compared with 19 (76%) of 25 bathroom sink cold taps (ANOVA; P < 0.05). Hot water taps were markedly less contaminated with only 3 (16%) of 19 kitchen and 6 (24%) of 25 bathroom sink taps positive (P < 0.05 compared with cold water equivalents). Bath taps, 5 (45%) of 11 cold and 2 (18%) of 11 hot taps, were also positive. Mixed taps were positive in two of seven kitchen, one of two bathroom sink, and two of four bath samples. Two of four shower samples were also positive. 
The FLA isolated were identified as Acanthamoeba spp., Hartmannella spp., Naegleria gruberi, Vahlkampfia sp., and Vannella sp. 2 Contamination of domestic water sources by Acanthamoeba spp. was found in 8 (30%) of 27 separate homes. Within these homes, five came from bathroom sink cold taps, one from a cloakroom cold tap, one from a bath hot-and-cold mixer tap and 1 from a bedroom sink mixer tap. In one patient’s home, all hot and cold taps in the kitchen, bathroom sink, and bath cold tap were positive for Acanthamoeba
mDNA Typing
In six of eight keratitis cases, identical HindIII mtDNA RFLPs were found for the Acanthamoeba isolate from the patient cornea and domestic tap water (Fig. 1) . Cox-PCR sequence comparison also confirmed the DNA relatedness of these clinical and tap-water–related strains (Fig. 2) . A reference strain of A. castellanii (CCAP 1501/1a) was included in the analysis and phylogenetic tree construction. 
In the acanthamoeba keratitis case from Belfast, Northern Ireland, Acanthamoeba spp. were isolated from the patient, the bedroom cold water tap of the patient’s accommodation, and the bathroom cold tap water of the parental home in the Irish Republic. Identical mtRFLPs and Cox-PCR sequences were found with the patient isolate and that from the Belfast tap water, but not that from the parental home (Pt-27) as shown in Figures 1 and 2
CL Habits
All 27 patients in the study returned questionnaires. Of these, 23 (85%) reported that they were CL wearers: 17 (77%) used soft lens types, and 6 (26%) gas-permeable lenses. None of the patients admitted to storing his or her lenses in tap water. However, all but three reported that their lenses or storage case occasionally came into contact with tap water. Twenty-four of 27 patients were aware of having water storage tanks on their roofs, including 20 of 23 of the CL–wearing patients. 
Of the eight homes from which Acanthamoeba were isolated, seven were occupied by CL wearers and all had roof storage tanks. Of these, four patients wore daily wear soft lenses, two disposable daily wear lenses, and one rigid gas-permeable lenses. Lens disinfection systems used were chlorine tablets (n = 1) one-step hydrogen peroxide (n = 3), and multipurpose solutions (n = 1). Two patients using daily wear disposable CLs used saline solution only for storage of the lenses. FLA were isolated from the tap water outlets of all the four non–lens wearers who had acanthamoeba keratitis. However, Acanthamoeba was isolated only from a bath mixer tap of one of the homes, the patient having had mud splashed into his eye at a motocross rally 3 days before evidence of infection. The strain from the tap was a different strain from that grown from his eye (Pt-22). 
Although acanthamoeba keratitis is now well recognized as an infection associated with CL wear and there have been significant improvements in CL care systems, the incidence within the UK remains significantly higher than in the remainder of Europe and the United States. 4 14 15 17 18 In this study, the hypothesis that domestic tap water is a reservoir for Acanthamoeba causing keratitis was investigated. The isolation of amoebae from the domestic tap water outlets of almost 24 (89%) of 27 of patient homes, of which 8 contained Acanthamoeba, demonstrates that this is a significant source of these organisms. Furthermore, the use of mtDNA typing methods for Acanthamoeba spp. strain differentiation confirmed that in six cases the patients’ domestic tap water was the source of infection. 
The taxonomic classification of the Acanthamoeba is based on morphologic observations of the trophozoite and cyst forms. 2 Although this permits the identification of the genus and most species it is a subjective approach and does not permit strain differentiation. 13 mtDNA RFLP typing has been shown to be a powerful technique for differentiating morphologically identical strains of Acanthamoeba and highlights the large degree of genetic diversity within species and strains classified by morphologic criteria. 13 20 However, the technique requires that the isolates be adapted to axenic (bacteria-free) broth media, which is not always successful with some strains. The methods for purifying mtDNA and the RFLP analysis are also time consuming and laborious. Alternative typing schemes have been developed based on nucleotide sequence analysis of the small subunit ribosomal RNA (ssrRNA) gene and, the 16S mitochondrial rDNA gene after PCR amplification. 25 26 This is a sensitive technique, requiring a few cells and can be performed with trophozoites grown on NNA-E. coli medium. This approach has been used to study taxonomic relationships within the genus and also the similarity of a patient isolate with isolates recovered from the domestic tap water in the home. 26  
In this study, we designed PCR primers to amplify a 1.2-kb portion of the mitochondrial cox1/2 gene for direct sequence analysis. 22 A large degree of nucleotide variation was found within the region, which permitted the differentiation of the eight patient isolates and, in six cases, demonstrated matching sequence homology with their respective tap water isolates. Studies are ongoing to establish whether this approach, including other mtDNA gene sequences, is a suitable method for Acanthamoeba taxonomic classification. Furthermore, the large copy number of mtDNA in Acanthamoeba would make this a potential target for developing PCR-based techniques for the rapid and sensitive diagnosis of acanthamoeba keratitis, and the cox1/2 gene may be suitable for this purpose. 27  
It should be noted that this survey was conducted retrospectively with some 3 to 10 months elapsing between the diagnosis of infection and obtaining tap water samples. If tap outlet colonization was an intermittent feature or occurred transiently only around the time of the patients’ infection, then more taps may have contained Acanthamoeba if sampling had been undertaken nearer to the time of diagnosis. Acanthamoeba levels in ground water have also been shown to fluctuate with seasonal temperature changes. 28 Although the acanthamoeba keratitis cases and tap water sampling occurred through all seasons, the possibility that tap water contamination is greater during the warmer months warrants investigation. It is also unlikely that the Acanthamoeba colonization is a feature only of the keratitis patient homes as the organism have been isolated from tap water outlets in England not associated with keratitis cases (Kilvington S, unpublished observations, 2003). 
A common feature of the samples positive for FLA was the presence of biofilm on the swab specimens taken from inside the tap outlets. Although not investigated further, direct microscopic examination of the biofilm revealed numerous bacteria and fungal hyphae besides FLA trophozoites and cysts. Therefore, tap water, particularly from tank-fed supplies, may also be a potential source of other forms of microbial keratitis. 29 FLA, including Acanthamoeba, have also been shown to support the intracellular growth and survival of pathogenic bacteria including Legionella pneumophila 30 31 Pseudomonas cepacia, 32 and Mycobacterium avium. 33 Accordingly, FLA in domestic water supplies may well serve as reservoirs for the presence and transmission of other human pathogens. 
The findings of this study may be explained by the domestic plumbing practices used in the United Kingdom by which the water mains feed potable water to the kitchen cold tap of the home, augmented by a water storage cistern located in the roof. This is a historical feature originally intended to store water when supplies to households were intermittent, and the feature is retained today for the purpose of supplying other water outlets in the home, such as the toilet cistern and the bathroom cold taps. 34 This arrangement is unique within the United Kingdom as in other European countries and the United States, all household taps are supplied directly by water mains. Only with the implementation of The Water Supply (Water Fittings) Regulations, 1999 has it been a requirement that the cistern should be covered with a “rigid, close fitting and securely fixed cover which is not airtight but which excludes light and insects from the cistern.” 35 The regulations are not retrospective and do not have to be applied to storage cisterns that were installed before this legislation. A poorly maintained, infrequently flushed, and uninsulated cistern can allow microbes, including Acanthamoeba, to proliferate in the water and hence colonize tap outlets. FLA, including one isolate of Acanthamoeba, were also made from taps supplied from water mains. This source is obtained directly from the water purification plant where it is passed through filter beds and chlorinated to render it safe and potable. It is unclear whether the FLA and Acanthamoeba detected from the water main–supplied taps originated directly from this supply or from within the home. 
In conclusion, domestic tap water, notably that supplied from roof storage cisterns, is a source of Acanthamoeba causing keratitis in the United Kingdom and gives some explanation as to why the incidence of acanthamoeba keratitis in this country is at least 15 times that of the United States and 7 times the rest of Europe. 15 14 18 None of the patients in this study admitted to rinsing or storing their lenses in tap water, suggesting that acanthamoeba keratitis can arise from indirect exposure to contaminated tap water. Even in compliant wearers, CL storage cases often contain bacteria and biofilm that provides a food source for Acanthamoeba. 7 36 CL wearers in the United Kingdom and visitors to the country should be aware of the risks from Acanthamoeba in tap water. Acanthamoeba keratitis remains a rare but serious consequence of CL wear. It is recommended that wearers adhere strictly to the manufacturer’s recommended lens hygiene procedures and use only sterile, approved solutions. In addition, the findings of this study indicate that the manipulation and storage of CLs, both for cleaning–disinfection purposes and insertion, should take place away from sources of potential contamination, such as bathrooms and other sites that receive water from roof storage tanks. 
Figure 1.
Acanthamoeba HindIII mtDNA RFLPs of corneal (c) and tap water (t) isolates from five patients (pt). DNA size marker (m) in kilobase pairs. With pt 27, (t1) is the Belfast tap isolate and (t2) that from the Irish Republic.
Figure 1.
Acanthamoeba HindIII mtDNA RFLPs of corneal (c) and tap water (t) isolates from five patients (pt). DNA size marker (m) in kilobase pairs. With pt 27, (t1) is the Belfast tap isolate and (t2) that from the Irish Republic.
Figure 2.
Phylogenetic tree of Acanthamoeba cox1/2-aligned sequences. A reference strain A. castellanii (1501/1a) was included in the analysis and phylogenetic tree construction.
Figure 2.
Phylogenetic tree of Acanthamoeba cox1/2-aligned sequences. A reference strain A. castellanii (1501/1a) was included in the analysis and phylogenetic tree construction.
Auran JD, Starr MB, Jakobiec FA. Acanthamoeba keratitis: a review of the literature. Cornea. 1987;6:2–26. [CrossRef] [PubMed]
Page FC. A New Key to Freshwater and Soil Gymnamoebae. 1988; The Freshwater Biological Association Cumbria, UK.
Bacon AS, Frazer DG, Dart JK, et al. A review of 72 consecutive cases of Acanthamoeba keratitis, 1984–1992. Eye. 1993;7:719–725. [CrossRef] [PubMed]
Radford CF, Minassian DC, Dart JK. Acanthamoeba keratitis in England and Wales: incidence, outcome, and risk factors. Br J Ophthalmol. 2002;86:536–542. [CrossRef] [PubMed]
Radford CF, Bacon AS, Dart JKG, Minassian DC. Risk factors for acanthamoeba keratitis in contact lens users: a case control study. BMJ. 1995;10:1567–1570.
Kilvington S, Larkin DF, White DG, Beeching JR. Laboratory investigation of Acanthamoeba keratitis. J Clin Microbiol. 1990;28:2722–2725. [PubMed]
Larkin DF, Kilvington S, Easty DL. Contamination of contact lens storage cases by Acanthamoeba and bacteria. Br J Ophthalmol. 1990;74:133–135. [CrossRef] [PubMed]
Seal D, Stapleton F, Dart J. Possible environmental sources of Acanthamoeba spp in contact lens wearers. Br J Ophthalmol. 1992;76:424–427. [CrossRef] [PubMed]
Stehr-Green JK, Bailey TM, Brandt FH, et al. Acanthamoeba keratitis in soft contact lens wearers: a case-control study. JAMA. 1987;258:57–60. [CrossRef] [PubMed]
Marciano-Cabral F, Cabral G. Acanthamoeba spp. as agents of disease in humans. Clin Microbiol Rev. 2003;16:273–307. [CrossRef] [PubMed]
De Jonckheere JF. Ecology of Acanthamoeba. Rev Infect Dis. 1991;13:S385–S387. [CrossRef] [PubMed]
Kingston D, Warhurst DC. Isolation of amoebae from the air. J Med Microbiol. 1969;2:27–36. [CrossRef] [PubMed]
Kilvington S, Beeching JR, White DG. Differentiation of Acanthamoeba strains from infected corneas and the environment by using restriction endonuclease digestion of whole-cell DNA. J Clin Microbiol. 1991;29:310–314. [PubMed]
Stehr-Green JK, Bailey TM, Visvesvara GS. The epidemiology of Acanthamoeba keratitis in the United States. Am J Ophthalmol. 1989;107:331–336. [CrossRef] [PubMed]
Radford CF, Lehmann OJ, Dart JK. Acanthamoeba keratitis: multicentre survey in England 1992–6. National Acanthamoeba Keratitis Study Group. Br J Ophthalmol. 1998;82:1387–1392. [CrossRef] [PubMed]
Mathers WD, Nelson SE, Lane JL, et al. Confirmation of confocal microscopy diagnosis of Acanthamoeba keratitis using polymerase chain reaction analysis. Arch Ophthalmology. 2000;118:178–183. [CrossRef]
Morlet N, Duguid G, Radford C, Matheson M, Dart J. Incidence of acanthamoeba keratitis associated with contact lens wear. Lancet. 1997;350:414–416. [CrossRef] [PubMed]
Seal DV, Beattie TK, Tomlinson A, Fan D, Wong E. Acanthamoeba keratitis. Br J Ophthalmol. 2003;87:516–517. [CrossRef] [PubMed]
Kilvington S, White DG. Acanthamoeba: biology, ecology and human disease. Rev Med Microbiol. 1994;5:12–20. [CrossRef]
Yagita K, Endo T. Restriction enzyme analysis of mitochondrial DNA of Acanthamoeba strains in Japan. J Protozool. 1990;37:570–575. [CrossRef] [PubMed]
Sambrook J, Fritsch EF, Maniatis T. Molecular Cloning: A Laboratory Manual. 1989; 2nd ed. Cold Spring Harbor Laboratory Press Cold Spring Harbor, NY.
Burger G, Plante I, Lonergan KM, Gray MW. The mitochondrial DNA of the amoeboid protozoon, Acanthamoeba castellanii: complete sequence, gene content and genome organization. J Mol Biol. 1995;245:522–537. [CrossRef] [PubMed]
Page RD. TreeView: an application to display phylogenetic trees on personal computers. Comput Appl Biosci. 1996;12:357–358. [PubMed]
Thompson JD, Higgins DG, Gibson TJ. CLUSTAL W: improving the sensitivity of progressive multiple sequence alignment through sequence weighting, position-specific gap penalties and weight matrix choice. Nucleic Acids Res. 1994;22:4673–4680. [CrossRef] [PubMed]
Ledee DR, Booton GC, Awwad MH, et al. Advantages of using mitochondrial 16S rDNA sequences to classify clinical isolates of Acanthamoeba. Invest Ophthalmol Vis Sci. 2003;44:1142–1149. [CrossRef] [PubMed]
Ledee DR, Hay J, Byers TJ, Seal DV, Kirkness CM. Acanthamoeba griffin: molecular characterization of a new corneal pathogen. Invest Ophthalmol Vis Sci. 1996;37:544–550. [PubMed]
Lehmann OJ, Green SM, Morlet N, et al. Polymerase chain reaction analysis of corneal epithelial and tear samples in the diagnosis of Acanthamoeba keratitis. Invest Ophthalmol Vis Sci. 1998;39:1261–1265. [PubMed]
Mathers WD, Sutphin JE, Lane JA, Folberg R. Correlation between surface water contamination with amoeba and the onset of symptoms and diagnosis of amoeba-like keratitis. Br J Ophthalmol. 1998;82:1143–1146. [CrossRef] [PubMed]
Dart J. Contact Lens and Prosthesis Infections. Tasman W Jaeger EA eds. Duane’s Foundations of Clinical Ophthalmology. 1996;2:1–30. Lippincott-Raven New York.
Abu Kwaik Y, Gao LY, Stone BJ, Venkataraman C, Harb OS. Invasion of protozoa by Legionella pneumophila and its role in bacterial ecology and pathogenesis. Appl Environ Microbiol. 1998;64:3127–3133. [PubMed]
Kilvington S, Price J. Survival of Legionella pneumophila within cysts of Acanthamoeba polyphaga following chlorine exposure. J Appl Bacteriol. 1990;68:519–525. [CrossRef] [PubMed]
Landers P, Kerr KG, Rowbotham TJ, et al. Survival and growth of Burkholderia cepacia within the free-living amoeba Acanthamoeba polyphaga. Eur J Clin Microbiol Infect Dis. 2000;19:121–123. [CrossRef] [PubMed]
Steinert M, Birkness K, White E, Fields B, Quinn F. Mycobacterium avium bacilli grow saprozoically in coculture with Acanthamoeba polyphaga and survive within cyst walls. Appl Environ Microbiol. 1998;64:2256–2261. [PubMed]
The Water Act 1989. 1989;ISBN 0105415898. HMSO London.
The Water Supply (Water Fittings) Regulations 1999. 1999;ISBN 0 11 082552 7. HMSO London UK.
Gray TB, Cursons RTM, Sherwan JF, Rose PR. Acanthamoeba, bacterial, and fungal contamination of contact lens storage cases. Br J Ophthalmol. 1995;79:601–605. [CrossRef] [PubMed]
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