The role of domestic tap water in Acanthamoeba contamination in contact lens storage cases in Korea

Article information

Abstract

INTRODUCTION

Acanthamoeba spp. are amphizoic protozoan parasites that are found in the environment as well as in tap water, contact lens cases, soil, dust, and air (Mergeryan, 1991; Armstrong, 2000). These amoebae are the causative agents of amoebic keratitis (AK), pneumonitis, and granulomatous amoebic encephalitis in immunocompromised hosts (Sell et al., 1997; Niederkorn et al., 1999; Rivera and Padya, 2002). AK was firstly reported by Nagington et al. (1974) in Great Britain and by Jones et al. (1975) in the United States. An AK epidemic occurred in the mid-1980s, which was attributed to the increased use of contact lenses and poor lens hygiene (Seal and Hay, 1993, 1994). Recent studies have shown that the rate of Acanthamoeba contamination in contact lens storage cases in Korea was 10.6-15.7% (Lee et al., 1997; Yu et al., 2001; Kong et al., 2002), which is a much higher rate than that reported in the west. Poor hygiene practices, such as the rinsing and storing of lenses in non-sterile saline or tap water are the main risk factors for lens case contamination (Stehr-Green et al., 1987; Seal et al., 1992). Prior to this report, there was no study on the source of Acanthamoeba contamination in contact lens storage cases in Korea. This study investigated the prevalence of Acanthamoeba in contact lens storage cases and domestic tap water in the Pusan province in an attempt to explain the source of Acanthamoeba contamination in contact lens storage cases in Korea.

MATERIALS AND METHODS

RESULTS

Acanthamoeba and FLA in tap water in the Pusan area

The FLA were isolated from 97 (46.9%) of the 207 domestic tap water samples, of which 12 (5.8%) contained Acanthamoeba, in the Pusan area (Table 1). The Acanthamoeba and FLA contamination rates at each water collection site were similar in this study (Table 1). However, they were more frequently isolated in community dwelling house types than in independent ones (Table 2).

Table 1.

Prevalence of Acanthamoeba and FLA contamination in domestic tap water samples

Table 2.

Prevalence of Acanthamoeba and other free-living amoeba contamination in domestic tap water samples from 2 house types

Acanthamoeba and FLA at filtration steps in the purification plants

The level of FLA contamination was examined at each filtration step in the purification plants using a three step system, which supplies domestic tap water to the survey area. Most FLA, including Acanthamoeba, were completely eliminated by the carbon filtration steps (Table 3). No FLA was detected in the water before it was supplied to houses.

Table 3.

Contamination from Acanthamoeba (above diagonal) and other free living amoeba (below diagonal) in water samples from each purification step of 3 water purification plants

DISCUSSION

AK is an infection that is associated with the wearing of contact lenses. There have been significant improvements in contact lens care systems. This study investigated the possible role of domestic tap water as a reservoir for Acanthamoeba contamination in contact lens storage cases.

In this study, Acanthamoeba was isolated from 5 (4.2%) in 120 contact lens storage cases. The contamination rates were lower than those reported in other provinces in Korea (Lee et al., 1997; Yu et al., 2001; Kong et al., 2002), but were similar to those reported in other countries (Larkin et al., 1990; Watanabe et al., 1994).

The contamination rate of FLA, including Acanthamoeba, in domestic tap water was investigated in order to determine the role of domestic tap water in Acanthamoeba contamination in contact lens storage cases. The FLA were isolated from 46.9% of the domestic tap water samples, of which 5.8% contained Acanthamoeba, in the Pusan area. These results demonstrate that domestic tap water is a significant source of these organisms. These results show a much lower Acanthamoeba contamination rate than in other countries. Kilvington et al. (2004) reported that FLA were cultured from one or more taps from 24 (89%) in 27 households of AK patients in UK. Of these, 8 (26.9%) contained Acanthamoeba. In Spain, Lorenzo-Morales et al. (2005) reported that Acanthamoeba contamination in 88 out of 148 (59.5%) tap water samples. The difference in the prevalence of Acanthamoeba contamination in tap water in different countries might be due to the difference in the tap water hygiene in each country. The Acanthamoeba and FLA were more frequently isolated in community dwelling house types than in independent ones. Community dwelling type houses and most independent ones in this survey area have water storage tanks, which are not often tightly covered. Therefore, environmental organisms can easily contaminate them.

Most FLA, including Acanthamoeba, was completely eliminated by the water purification steps in water purification plants. This shows that FLA contamination, including that from Acanthamoeba, in domestic tap water does not originate from the purification plant, but from the water storage tanks.

Previous studies have shown that many Acanthamoeba isolated from tap water and seawater sources might have some pathogenic ability (Kilvington et al., 2004; Lorenzo-Morales et al., 2005). In addition, some Acanthamoeba isolated in this study have similar molecular characteristics to those of the clinical isolates (data not shown).

In conclusion, domestic tap water, especially when supplied from roof storage tanks, is a source of Acanthamoeba contamination. Contact lens wearers should be aware of the risks associated with Acanthamoeba in tap water supplied from water storage tanks. More education about the hygienic maintenance of water storage tanks is recommended.

Article information Continued