Updated on 6/24/19, 8/14/21, and 8/18/22
Heterotrophs are as micro-organisms that require organic carbon for growth (WHO 2017).
Heterotrophic Plate Count (HPC) — aka “standard plate count,” “total bacterial count,” and several other terms — are bacteria colony counts detected by using a simple, culture test on an organic carbon medium (Allen 2004, WHO 2017). The bacteria population recovered in HPC tests can vary widely with temperatures, incubation times, nutrients, and methods used by the laboratory.
People are exposed to HPC bacteria much more from food than from water (Allen 2004, WHO 2003). Tens of thousands of colony forming units (CFUs) per gram or milliliter have been found in dairy, meat, and vegetable products (Reynolds 2002).
HPC versus pathogens
Nearly all disease-causing (pathogenic) bacteria are heterotrophic. Some pathogens can be grown on media typically used for HPC tests but other pathogens (e.g., Legionella; nontuberculous mycobacteria) can be distinguished only by using special media and techniques (Allen 2004, WHO 2003).
Donahue found that Legionella pneumophila positivity was higher in water with HPC concentrations ranging from 101–1000 CFU/mL than in water with HPC exceeding 1001 CFU/mL, but found no consistent relationship between HPC and Legionella pneumophila in domestic (potable) water (Donahue 2021). Although some studies have suggested high levels of harmless HPC bacteria can reduce pathogens (Camper 1985, Payment 1991, Payment 1997), one cannot know what percentage of an HPC count from a building water system is harmless versus disease-causing bacteria, so high HPC should not be considered protective. Moreover, Legionella and mycobacteria have been found more often in potable water samples with high HPC (Donahue 2019).
A literature review by a group from AWWA, EPA, and Yale concluded that HPC can be useful for monitoring the effectiveness of water treatment and changes in bacterial water quality, but setting an upper limit for HPC in drinking water cannot be justified based on health risk (Allen 2004). Similarly, a group of public health experts and microbiologists convened by WHO and NSF International to discuss the role of HPC in managing water systems reached a consensus that there is “no evidence, either from epidemiological studies or from correlation with occurrence of waterborne pathogens, that HPC values alone directly relate to health risk” (WHO 2003).
The role of HPC in water management programs (WMPs)
Although HPC has not been found to correlate directly with pathogens, it can be used to assess conditions (e.g., stagnation, disinfection) that affect microbial growth in a building water system (AWWA 2020, Donahue 2021).
The maximum level of HPC allowed in US public water systems without filtration is 500 CFU/mL (per the US EPA Safe Drinking Water Act), but a maximum HPC level in building plumbing (potable) systems has not been defined. The threshold of 500 CFU/mL was originally established based on studies showing the effect of HPC on total coliform tests–it was not based on evidence of health risk above 500 CFU/mL (Allen 2004).
For the type of water management program (WMP) outlined in ANSI/ASHRAE Standard 188 and the Centers for Disease Control and Prevention (CDC) toolkit (CDC 2017)—and required for hospitals and nursing homes that receive reimbursements from the Centers for Medicare & Medicaid Services (CMS)—tests are generally performed for one of two purposes:
- To validate the overall effectiveness of the WMP in accomplishing its primary objective (e.g., to minimize Legionella), or…
- To monitor the performance of a control measure. For example, if a WMP control measure is to maintain hot water temperatures at all faucets within a certain range (limit), temperatures could be measured at faucets periodically to see if they are within that range.
The distinction between validation tests and control measure performance tests is important in determining the role of HPC in a WMP.
For a water management program (WMP) designed to minimize Legionella risk, consider each water system type separately–based on scientific evidence, guidelines, and best practices–in deciding the role of HPC tests for control measure monitoring or WMP validation.
Plumbing (domestic water) systems
Studies have shown no direct or consistent correlation between HPC results and Legionella in domestic hot or cold water systems. Within biofilms, however, van der Kooij found Legionella colony count correlated significantly with HPC as well as with the total cell count (TCC) and adenosine triphosphate (ATP) concentration (van der Kooij 2017). As mentioned above, Donahue’s data showed that Legionella and Mycobacterium species were found more often in water samples with high HPC (Donahue 2019). Selvaratnam did not find a significant correlation between HPC and Legionella, mycobacteria, or Pseudomonas (Selvaratnam 2018).
Although there is not enough evidence to assume pathogen control based solely on negative or low HPC tests, comparing HPC and pathogen test results for a given facility’s domestic water system could provide useful information. For example, seeing a consistent correlation could allow a facility to make use of HPC test results between Legionella sampling rounds.
WHO points out that HPC tests can indicate stagnation, inadequate temperatures, or low disinfectant levels in domestic water systems but other tests (e.g., temperature; chlorine) will likely be more useful for control measure monitoring.
Data studied by Dr. Richard Miller of the University of Louisville (Miller 2002) have shown HPC to be a good indirect indicator of Legionella in whirlpool spas. Although Legionella tests will provide more direct and reliable feedback on Legionella concentrations in whirlpool spas, HPC tests could be used as an additional (and perhaps more frequent) validation test. ASHRAE Guideline 12-2020 (section 7.4.1) and ASHRAE Standard 188 (section 188.8.131.52) recommend a maximum HPC level of 200 CFU/mL in spas.
HPC tests should not be used to validate Legionella control in cooling tower systems because studies have shown no reliable correlation between HPC and Legionella counts. In Garnett’s study of 100 cooling towers, Legionella counts greater than 100 CFU/mL were found only in towers with an HPC exceeding 10,000 CFU/mL and Legionella counts higher than 1,000 CFU/mL were found only in towers with an HPC exceeding 100,000 CFU/mL (Garnett 1993). But of the 1,100-plus towers studied by Miller, towers that tested positive for Legionella generally had a lower HPC than towers that tested negative. What’s more, some of the towers with extremely high Legionella counts had an HPC near zero (Miller 1993). Witherell found the same results as Miller—high Legionella counts with low HPC—indicating certain water treatment programs may reduce bacteria competing with Legionella for food, but not reduce Legionella, allowing Legionella to flourish (Witherell 1986).
Although they are not an appropriate validation method for Legionella in cooling towers, HPC tests may be required by regulations (e.g., in New York) and have been recommended for monitoring cooling tower treatment (CTI 2008; WHO 2007).
How do you use HPC in your water management program? Please comment below.
For Additional Reading
Allen M, Edberg S, Reasoner D. 2004. Heterotrophic plate count bacteria–what is their significance in drinking water? International Journal of Food Microbiology 92: 265-274
ASHRAE. 2021. Legionellosis: Risk Management for Building Water Systems. Atlanta: American Society of Heating, Refrigerating and Air-Conditioning Engineers. Available for purchase at Legionellosis: Risk Management for Building Water Systems
ASHRAE. 2020. Guideline 12-2020. Managing the Risk of Legionellosis Associated with Building Water Systems. Atlanta: American Society of Heating, Refrigerating and Air-Conditioning Engineers.
AWWA. 2020. Responding to Water Stagnation in Buildings with Reduced or No Water Use. American Water Works Association.
Camper AK, et al. 1985. Growth and Persistence of Pathogens on Granular Activated Carbon Filters. Appl. Environ. Microbiol. 50:6, 1378-1382.
CDC. 2017. Developing a Water Management Program to Reduce Legionella Growth & Spread in Buildings: A Practical Guide to Implementing Industry Standards. Atlanta: Centers for Disease Control and Prevention. Available at Developing a Water Management Program to Reduce Legionella Growth & Spread in Buildings
CTI. 2020. Legionellosis Guideline: Practices to Reduce the Risk of Legionellosis from Evaporative Heat Rejection Equipment Systems. Houston, TX: Cooling Technology Institute.
Donohue M, Vesper S, Mistry J, Donohue J. 2019. Impact of Chlorine and Chloramine on the Detection and Quantification of Legionella pneumophila and Mycobacterium Species. Appl Environ Microbiol 85:e01942-19..
Donohue M. 2021. Quantification of Legionella pneumophila by qPCR and culture in tap water with different concentrations of residual disinfectants and heterotrophic bacteria. Science of The Total Environment 774, 145142.
Garnett HM, Gilmore K, Liu J. 1993. Legionella: An Unwelcome Pollutant. Environmental Technology 11; 393-400.
Reynolds KA. 2002. HPC Bacteria in Drinking Water: Public Health Implications? Water Conditioning & Purification, July.
Miller RD, Kenepp KA. 1993. Risk Assessments for Legionnaires Disease Based on Routine Surveillance of Cooling Towers for Legionellae. Presented at the 4th International Symposium on Legionella, 1992. In: Barbaree, J. M., R. F. Breiman, and A. P. DuFour, eds. Legionella: Current Status and Emerging Perspectives. Washington, D.C.: American Society for Microbiology; 40-43.
Miller RD, Koebel DA. 2002. Prevalence of Legionella in Whirlpool Spas: Correlation with total bacteria numbers. In: Marre R, et al, eds. Legionella. Washington, DC: ASM Press, 275-279.
Payment P, Richardson L, Siemiatycki J, et al. 1991. A Randomized Trial to Evaluate the Risk of Gastrointestinal Disease due to Consumption of Drinking Water meeting current Biological Standards. American Journal of Public Health vol. 81, no. 6.
Payment P, Siemiatycki J, Richardson L, et al. 1997. A Prospective Epidemiological Study of the Gastrointestinal Health Affects due to the Consumption of Drinking Water. International Journal of Environmental Health Research 7, 5-31.
Witherell LE, Novick LF, Stone KM, et al. 1986. Legionella in Cooling Towers. Journal of Environmental Health, November/December; 134-139.
Rusin P, Rose J, Haas C, Gerba C. 1997. Risk assessment of opportunistic bacterial pathogens in drinking water. Rev Environ Contam Toxicol. 152:57-83.
Selvaratnam S, Coughlin M, Sotkiewicz E. 2018. Practical Recommendations for Meeting the Objectives of the CMS Memorandum. Presented at the annual convention of the Association of Water Technologies.
van der Kooij D, Bakker G, Italiaander R, et al. 2017. Biofilm Composition and Threshold Concentration for Growth of Legionella pneumophila on Surfaces Exposed to Flowing Warm Tap Water without Disinfectant. Appl Environ Microbiol 83:e02737-16.
WHO. 2003. Heterotrophic Plate Counts and Drinking-water Safety: The Significance of HPCs for Water Quality and Human Health. Published on behalf of the World Health Organization by IWA Publishing, London. Available at Heterotrophic Plate Counts and Drinking-water Safety.
WHO. 2007. Legionella and the prevention of legionellosis. Geneva: World Health Organization. Available at Legionella and the prevention of legionellosis.
WHO. 2017. Drinking Water Parameter Cooperation Project. Support to the revision of Annex I Council Directive 98/83/EC on the Quality of Water Intended for Human Consumption (Drinking Water Directive). Available at Drinking Water Parameter Cooperation Project.