Comparative evaluation of biofilm disinfectant efficacy tests
Introduction
Biofilm bacteria live in a self-organized, cooperative community of microorganisms attached to surfaces, interfaces, or each other, embedded in a matrix of extracellular polymeric substances of microbial origin, and exhibit altered phenotypes with respect to growth rate and gene transcription (Boles et al., 2004, Donlan and Costerton, 2002, Stoodley et al., 2002). Biofilms are prevalent in moist or aqueous environments, even if the surfaces are intermittently dehydrated. Bacteria predominantly exist as biofilm (Costerton et al., 1978, Costerton, 2004, Donlan and Costerton, 2002). Biofilm bacteria are different from their planktonic counterparts (Loo et al., 2000, Sauer et al., 2002, Sternberg et al., 1999).
Biofilm bacteria are notoriously tolerant to conventional chemical disinfectants (Donlan and Costerton, 2002, Stewart et al., 2000). These high tolerances may be caused by slow diffusion through the extracellular polymeric substance matrices, the existence of persister cells, development of resistant phenotypes, and adaptations to micro-environments (Spoering and Lewis, 2001, Stewart et al., 2000). Because detached biofilm clumps retain this increased resistance (Fux et al., 2004) and may contain enough bacteria to give an infective dose (Wilson et al., 2004), biofilm bacteria represent a potential health risk (Armon et al., 1997, Murga et al., 2001).
For these reasons, there is a recognized need for laboratory methods for testing the efficacy of chemical disinfectants against biofilm bacteria. The standard methods used to show potential antibiofilm activity of chemical disinfectants often employ the use of planktonic cells that have been dried on a hard surface carrier (ASTM International, 2003). However, a test against actual biofilm bacteria is required for relevancy to real-world applications (Bloomfield and Sims, 1996, Costerton, 2004, Costerton and Stewart, 2001, van Klingeren et al., 1998). Not only must a biofilm disinfection test method include all the biological, chemical, and analytical components of conventional suspension or dried surface tests, but the method also requires some engineered apparatus, such as a biofilm reactor, for growing a reproducible biofilm. Moreover, the laboratory biofilm should be grown so that it possesses the key attributes of the naturally-occurring biofilm where the disinfectant will be applied.
Fluid dynamics are an important consideration when designing a reactor to grow a relevant biofilm (Purevdorj and Stoodley, 2004). A biofilm will self-assemble into a characteristic architecture that depends upon the fluid shear conditions under which it grew. For example, biofilms formed under high shear, turbulent flow, are stronger, more stable, and more strongly attached than their low shear, laminar flow counterparts (Pereira et al., 2002, Purevdorj et al., 2002, Vieira et al., 1993). Biofilms grown in turbulent flow conditions have a greater mass, physiological activity, and total protein than biofilms grown in laminar flow (Simões et al., 2003a, Simões et al., 2003b). Biofilms grown in turbulent flow are more dense than the fluffy biofilms grown in laminar flow (Pereira et al., 2002). It would be prudent to engineer fluid dynamics within the biofilm growth reactor that emulate the fluid dynamics in the target environment (Blanchard et al., 1998, Eginton et al., 1998, Simões et al., 2003a, Simões et al., 2003b, Simões et al., 2005).
A variety of reactors and growth systems have been used successfully for research and/or disinfectant testing purposes (e.g., Ceri et al., 1999, Characklis, 1990, Charaf et al., 1999, Gilbert et al., 1998, Goeres et al., 2005, Kharazmi et al., 1999, Luppens et al., 2002, Pitts et al., 2003, Stoodley and Warwood, 2003, Wilson, 1999, Zelver et al., 1999). For the development and official registration of commercial disinfectants against biofilm bacteria, standardized laboratory reactors and associated standard operating procedures are required. The standardization process for biofilm tests has just begun. At present, only one biofilm reactor and operating procedure has been approved by the USA standard setting organization American Society for Testing and Materials International (ASTM), method #E 2196-02 (ASTM International, 2002). Tests of antibiofilm efficacy are based predominantly on ad hoc disinfectant testing methods.
The main goal of this study was to compare the efficacy results for three biofilm disinfectant tests, where each test utilized a different type of reactor fluid dynamics: turbulent flow, laminar flow, and no flow. Also included in the comparative study were disinfectant challenge tests against dried biofilm and a current hard surface carrier test method. Each biofilm growth reactor and associated test method chosen for this comparative study has potential for standardization, and consequently is a candidate method for the development, testing and registration of antibiofilm disinfectants. Therefore, the results include the statistical characteristics, such as the mean viable cell density on control carriers and the repeatability SD for LR values, for each of the individual tests.
Section snippets
Bacterial species/strains and inoculum preparation
Pseudomonas aeruginosa ATCC 15442 were grown in 300 mg tryptic soy broth (TSB) l− 1 and Staphylococcus aureus ATCC 6538 were grown in 30 g TSB l− 1. Both were incubated for 18–24 h in a 37 °C shaker. Bacteria were transferred no more than 5 times from the original culture stock.
Coupons and cleaning procedure
All five test methods used borosilicate glass coupons, which were disks having a diameter of 1.27 cm and a height of 0.4 cm (BioSurface Technologies, Corp., Bozeman, MT). Prior to use, the coupons were visibly inspected
Comparing LR values among the five test methods
The mean LR values for each of the five test methods for each of the six treatments for each species are shown in Fig. 2. In each panel of Fig. 2, the spread of LR values among test methods covers a range of at least 4 logs.
Discussion
The challenge when estimating “real-world” efficacy in the laboratory is deciding which factors most influence the outcome, then choosing a method that incorporates those factors as part of the test. Biofilms grow in diverse and dynamic environments where factors such as fluid shear are important. The results of this investigation convincingly demonstrated that biofilm reactor choice is critical. Biofilm grown under high fluid shear conditions (CDC) produced the smallest LR, biofilm grown in
Acknowledgments
This research was supported by the U.S. Environmental Protection Agency (EPA) under contract #68-W-02-050 with Montana State University and by the Industrial Associates of the Center for Biofilm Engineering (CBE). The findings and conclusions in this report are those of the author(s) and do not necessarily represent the views of the US EPA.
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